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JP3439701B2 - Production method of wood raw material compost - Google Patents
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JP3439701B2 - Production method of wood raw material compost - Google Patents

Production method of wood raw material compost

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Publication number
JP3439701B2
JP3439701B2 JP30897299A JP30897299A JP3439701B2 JP 3439701 B2 JP3439701 B2 JP 3439701B2 JP 30897299 A JP30897299 A JP 30897299A JP 30897299 A JP30897299 A JP 30897299A JP 3439701 B2 JP3439701 B2 JP 3439701B2
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JP
Japan
Prior art keywords
compost
nitrogen
raw material
wood
fermentation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
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JP30897299A
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Japanese (ja)
Other versions
JP2001130991A (en
Inventor
芳夫 井汲
郁夫 渡邊
利夫 古谷
正昭 杉本
紘雄 大塚
暢英 藤嶽
武志 鈴木
昌太郎 岡本
博一 宇治原
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Kansai Electric Power Co Inc
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Kansai Electric Power Co Inc
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Priority to JP30897299A priority Critical patent/JP3439701B2/en
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Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • C05F9/04Biological compost
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/145Feedstock the feedstock being materials of biological origin
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Molecular Biology (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)
  • Fertilizers (AREA)

Description

【発明の詳細な説明】 【0001】 【発明の属する技術分野】この発明は、肥料や土壌改良
資材に利用される堆肥の製造方法に関し、詳しくは腐植
化に必要な有機質炭素源として木質を含有する木質原料
堆肥の製造方法に関する。 【0002】 【従来の技術】一般に、木質原料堆肥は、おがくずや木
材チップなどの木質物を入れた堆肥のことをいい、例え
ば木質の廃材を有効に利用した堆肥である。 【0003】しかし、木質原料は、その表面が充分に腐
熟しているように見えても内部は未熟な場合が多く、土
壌に施用した後に表層の腐植質部分が先に微生物分解し
てしまうと、内部の未熟な木質が剥き出しになり、この
木質の分解時に土壌中の窒素を多量に消費する。そのた
め、このような木質原料堆肥は、施用量が多すぎると土
壌がいわゆる窒素飢餓を起こすという危険性を有する。 【0004】木質原料は、通常の堆肥の有機質炭素源で
ある籾殻、稲わら、落ち葉の分解速度よりかなり遅く分
解する。例えば、自然状態で土壌に混合されたおがくず
が、充分に腐熟してそれを分解するために土壌微生物が
窒素を要求しなくなるまでには30年近い年月が必要で
あるといわれている。 【0005】土壌より温度の高い堆肥化条件では、おが
くずなどの木質原料が分解される速度は速くなるが、そ
れでも3〜5ヶ月間堆肥化した木質原料を施用して窒素
を取り込まなくなるまでには2年くらいの期間を要す
る。 【0006】ところで、石炭灰は、火力発電所の運転に
伴ってわが国内で年間約550万t発生するが、その8
0%をフライアッシュが占めている。フライアッシュ
は、その発生量の50〜60%がセメントの添加剤とし
て利用されてきた。一方、クリンカアッシュは、道路の
路床材などといった土木用途に利用される他、酸性土壌
の改良剤としてそのまま直接に散布されているに過ぎな
い。 【0007】 【発明が解決しようとする課題】前述のように、堆肥を
製造する場合に木質原料を有機質炭素源として利用する
ことは良い堆肥を短期間に製造するためには必ずしも好
ましいことではなく、木質原料堆肥を短期間で確実に窒
素飢餓を起こさない程度に腐熟させることは容易なこと
ではなかった。 【0008】また、上記した木質原料の堆肥化にともな
う問題は、難分解性の木材の芯材を含む伐採木チップの
ような木材チップを利用する場合に特に顕在化する。 【0009】一方、石炭灰の一種であるフライアッシュ
およびクリンカアッシュは、強アルカリ性であるため
に、有効利用できる分野が限られており、大量に消費さ
れる利用分野の開拓が求められていた。 【0010】そこで、この発明の課題は、上記した問題
点を解決して、 充分に腐熟した状態の木質原料堆肥を短
期間で確実に製造できるようにすることである。また、
火力発電所などの副産物により多量に発生する石炭灰を
有効利用でき、これにより肥料効果の高い木質原料堆肥
が得られるようにすることである。 【0011】 【課題を解決するための手段】上記の課題を解決するた
め、この発明においては、チップ材1m 3 からなる炭素
源に対して、水および窒素源として鶏糞25〜50kg
を混合し、さらにクリンカ25〜150kgを添加混合
し、この混合物を大気中で発酵させて腐植化する木質原
料堆肥の製造方法を採用することができる 【0012】この発明の木質原料堆肥の製造方法では、
木質を含む有機質の炭素源に水および窒素源に対してク
リンカのような石炭灰を添加混合することにより、2
週〜30週程度かけて発酵させた堆肥の硝酸態窒素含
量、炭素率を好ましい値に誘導することができ、所期し
た腐熟が充分に進行した状態にすることができる。 【0013】このように石炭灰の添加によって腐植化の
速度が速まる理由については未だ充分に立証されてはい
ないが、例えば微生物発酵によって特に初期のセルロー
ス分解時期に堆肥内部は60〜80℃に昇温し、そのと
きに多孔質の石炭灰が触媒のような働きをし、石炭灰の
表面では熱化学反応による有機質の分解反応が起こりや
すくなっているとも考えられる。また、石炭灰は、アル
カリ性を示すものであるから、これを添加混合すること
によって発酵により生成する有機酸を中和して堆肥原料
全体のpHをアルカリ側に調整することができ、これに
より弱アルカリ性環境を好む微生物の良好な発育環境が
つくられているとも考えられる。 【0014】また、木材チップやおがくずなどの木質
は、炭素含量が多く、これを腐熟させるためには、窒素
分を添加する必要がある。 【0015】そして、上記の木質原料堆肥の製造方法に
おいて、窒素源として鶏糞を採用すると、堆肥成分とし
て不足しがちな窒素ばかりでなく、リン酸、カルシウム
の含量をも充分に高めることができる。 【0016】 【発明の実施の形態】この発明に用いる木質を含む有機
質炭素源は、チップ材などの木質からなる有機質炭素
含有し、その他に籾殻、稲わら、笹、落ち葉、ススキ
等の雑草その他の植物質、または牛、馬、豚、鶏などの
家畜の糞などの生物由来の有機質であって、堆肥原料と
して従来使用可能なものを併用し、例えば都市の生ゴミ
のコンポストを利用することもできる。 【0017】また、チップ材などの木質材料は、微生物
分解をできるだけ速やかに進行させるために、破砕機を
用いて繊維化されたものであることが好ましい。このよ
うな繊維化された木質を工業的に製造するには、タブグ
ラインダーと呼ばれる擦り潰し機能を有する破砕機を用
いることが好ましい。 【0018】この発明に用いる窒素源は、特に限定され
た種類のものではなく、特に好ましい鶏糞の他、尿素肥
料や石灰窒素肥料など、周知の肥料を用いることができ
る。 【0019】次に、この発明に用いる石炭灰は、石炭の
灰分、すなわち石炭の熱分解または酸化生成物をいい、
通常、石炭を燃焼させた後に残る灰分である。多量の石
炭灰は、火力発電所からの石炭灰廃棄物(クリンカアッ
シュまたはフライアッシュ)として産出するので、資源
の有効利用を図り、かつ安定した品質の土壌改良資材を
提供するためにこれらを利用することが好ましい。 【0020】 【0021】また、この発明でいうクリンカ(クリンカ
ーとも呼ばれる)は、石炭を焼成したときに、石炭中の
融点の低い部分が溶けて全体を固まらせ、塊状になった
石炭灰であり、フライアッシュとほぼ同様の成分からな
るものと考えられる。このようなクリンカは、均一に混
合して効率よく作用させるために、5mm以下程度の粒
径に整粒されたものを用いることが好ましい。 【0022】 【0023】また、この発明で混合物に添加する水は、
微生物発酵などの有機質の分解に所要量の水分であり、
堆肥が乾燥せず窒素成分やカリウムなどの水溶成分が流
失しない程度の適量の水分を適宜に補充する。また、過
剰の水分が堆肥内に存在すると好気性微生物の生育が妨
げられ嫌気性菌のみの活動が活発化するので、堆肥下部
から堆肥重量で絞り出された水が適当に排水されるよう
に、盛土された基台、コンクリート製の堆肥盤、簀の子
状の排水台などを利用することが好ましい。 【0024】有機質炭素源と石炭灰とを混合すると共に
加水し、自然醗酵により、順に糖分解、セルロース分
解、リグニン分解を起こさせるが、特に糖分解期、セル
ロース分解期には醗酵熱が発生する。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堆肥内温度条件
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。 【0025】因みに、有機物の腐熟過程初期の糖分解期
には、タンパク質、アミノ酸、糖質などの比較的分解さ
れ易い物質が分解されるが、この時期には好気性の糸状
菌や細菌が作用する。次いで、セルロース分解期には、
ヘミセルロースを分解するテルモアクチノミセス等の高
温性好気性の放線菌やセルロース分解菌が増殖し、醗酵
熱を発生させる。その時期を過ぎると温度は低下し、担
子菌等によりリグニンが分解されるようになる。 【0026】有機質の炭素源としての木質、石炭灰のク
リンカ、窒素源およびそのうちの鶏糞についての好まし
い配合割合は、例えば木質として摩砕され繊維がほぐさ
れた状態のチップ材である場合は、その1m3 (比重が
約0.5であれば約500kg)に対して、石炭灰25
〜150kg(好ましくは、クリンカ25〜150k
g)、窒素源5〜20kg(好ましくは尿素5〜10k
g、石灰窒素10〜20kg、鶏糞25〜50kg)で
ある。 【0027】石炭灰の配合割合が上記した所定範囲未満
の少量では、堆肥腐熟促進の効果が殆どなく、上記所定
範囲を越えて多量に配合すると、クリンカでは保水性が
悪くなり、これらの場合は微生物の生育を阻害するので
好ましくない。 【0028】窒素源の配合割合が、上記所定範囲未満の
少量では、発酵時に増殖する微生物の体を構成する窒素
分の不足を招き、発酵不良となって好ましくなく、上記
所定範囲を越えて多量に配合すると、発酵初期に高温発
酵が長時間続き、窒素分の無機化が激しく進行するが、
微生物体に取り込まれる窒素分は同じ程度に増加せず、
その結果、発酵促進剤として添加した窒素分がアンモニ
アガスとして大気中に放出されて有効に利用されない現
象が発生することになって好ましくない。 【0029】 【実施例および比較例】〔実施例1〜3、比較例1〜
6〕 炭素源として、木質廃材をタグラインダーで磨り潰す
ように破砕することにより繊維をほぐしたチップ材(比
重約0.5)、窒素源および石炭灰(クリンカ)を表1
に示す比率で混合し、強制給排気方式の堆肥化装置(川
鉄商事社製:養土くん、円筒型のシート張り枠体内に給
排気ポンプに接続した多孔性配管を埋設した装置)に投
入し、混合材料の含水量が約70%になるように水分を
添加し、給排気ポンプにより10分/3時間毎に強制通
気を行なって好気的に発酵させることにより、混合物内
部温度を1週間にわたり65〜75℃になるように保温
した。 【0030】次いで、4〜5ヵ月間55〜75℃の内部
温度になるように水分量および強制通気を調整して好気
発酵させた後、内部温度が50〜40℃に下降したとき
に好気的な初期発酵が終了したことを確認した。 【0031】その後、堆肥化装置から好気発酵済の堆肥
を搬出し、野積み状態で約2〜5ヵ月の間、後熟させて
堆肥を製造した。 【0032】 【表1】【0033】実施例および比較例に用いたクリンカアッ
シュの組成は以下の通りである。 【0034】クリンカアッシュ:SiO2 40〜75
%、Al2 3 15〜35%、Fe23 2〜20%、
CaO 1〜10%。 【0035】以上の条件で堆肥を製造する実施例および
比較例の試験期間中に、腐熟の進行状態を調べるため、
乾式燃焼法によって全炭素含量と全窒素含量を調べると
共に炭素率(C/N比)を算出し、アンモニア態窒素含
量と硝酸態窒素含量をブレムナー法で測定した。また、
10ヵ月後の堆肥については、キノリン重量法でリン全
量(P2 5 %)を測定すると共に、原子吸光測定法に
よってカリウム(K2O%)、カルシウム全量(CaO
%)を測定した。また、発酵時間が5、7または10カ
月の堆肥試料を培土資材検定法に従って幼植物試験を行
なった。 【0036】これらの試験結果については、以下の通り
である。 【0037】すなわち、図1および図4の図表に示す結
果からも明らかなように、比較例に比べて実施例は、試
験期間の第22週目から第31週目にかけて硝酸態窒素
含量(NO3 −N、mg/100g)が増加した。特
に、実施例2、3については、顕著に硝酸態窒素含量は
増加し、腐熟が急速に進行していることがわかる。 【0038】また、図2および図5の結果からも明らか
なように、比較例に比べて実施例は、第22週目から第
31週目にかけての炭素率が低い値であり、腐植化が進
行していることがわかる。 【0039】 【表2】 【0040】また、表2の結果からも明らかなように、
石炭灰と鶏糞を併用して添加した実施例3の堆肥では、
リン、カリウム、カルシウムの含量が著しく高く、これ
らの肥料必須要素を植物に充分に供給するには、鶏糞の
使用が適当であることがわかる。 【0041】次に、図3および図6には、腐植の良否を
判定可能であることが知られているPQ値の経時変化を
示した。 【0042】ここで、PQ値とは、熊田恭一著の「土壌
有機物の化学」、第124〜127頁にも記載されてい
るように、沈殿部割合とも別称され、土壌や堆肥からN
aOHまたはNa4 2 7 を溶媒として抽出された腐
植のうち、腐植酸の占める割合(%)をいい、以下の式
で示される値である。 【0043】 PQ値(%)=〔a/(a+b)〕×100 (式中、a、bは、それぞれ堆肥1gに相当する腐植酸
およびフルボ酸の0.1N KMnO4 消費量(ml)
である。) 【0044】図3および図6の結果からも明らかなよう
に、比較例4〜6のPQ値に比べて実施例1または実施
例3のPQ値は、試験期間の第22週目から第31週目
にかけて顕著に高くなっており、植物の育成に有用な腐
植酸とフルボ酸の含有量が高い物性が短期間に得られて
いることがわかる。 【0045】次に、幼植物試験では、好気的発酵直後の
堆肥、野積後2ヶ月または5ヶ月後の堆肥を一定量混ぜ
た土壌に「シロナ」(アブラナ科植物)の幼苗を30〜
40日間、室温25℃±5℃に管理された温室において
遮光せず適宜に潅水するという環境で育成し、実施例3
および比較例5、6の堆肥による生育量(地上部と根系
の合計重量)を比較した。また、生育量は、水分の含有
量の影響を排除するために、遮光条件下および外気が入
る換気条件下で2週間の条件で乾燥させたものも併せて
測定した。また、対照区として通常の堆肥(石炭灰を添
加しなかったもの)を同量混合したこと以外は全く同様
の条件で「シロナ」を育成し、その生育量(地上部と根
系の合計重量)を100%とした場合における実施例3
と比較例5、6の生体重量を表3に示した。 【0046】 【表3】 【0047】表3の結果からも明らかなように、PQ値
の高い実施例3の堆肥の生体重量は比較例5、6に比べ
て高くなっており、PQ値の高い(63.3以上)の実
施例の堆肥は、植物育成能力が高い。これらのことか
ら、堆肥に石炭灰を添加して腐植化することにより、有
機物を単に堆肥化したものに比べて肥料効果の高い堆肥
が生成したことが、幼植物検定試験によって確認でき
た。 【0048】 【発明の効果】この発明は、以上説明したように、木質
を含む有機質の炭素源に水、窒素源および石炭灰を混合
し、この混合物を大気中で発酵させて腐植化する堆肥の
製造方法としたので、第20週〜30週程度という比較
的短期間で発酵させた堆肥の硝酸態窒素含量、炭素率を
好ましい値に誘導することができ、植物の育成に好まし
い影響を与える充分に腐熟した状態の木質原料堆肥を短
期間で確実に製造できるという利点がある。 【0049】また、この発明の木質原料堆肥の製造方法
では、火力発電所などの副産物により多量に発生するク
リンカからなる石炭灰を有効に利用でき、これにより得
られる肥料が効果の高い堆肥になるという利点もある。 【0050】また、上記の木質原料堆肥の製造方法にお
いて、窒素源として鶏糞を採用した発明では、上記した
利点に加えて堆肥成分として不足しがちな窒素ばかりで
なく、リン酸、カルシウムの含量をも充分に高めること
ができる利点もある。
Description: BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing compost used as a fertilizer or a soil improvement material, and more particularly to a method of containing wood as an organic carbon source necessary for humification. The present invention relates to a method for producing a woody raw material compost. 2. Description of the Related Art In general, woody raw material compost refers to compost containing woody materials such as sawdust and wood chips, and is, for example, a compost effectively utilizing woody waste material. [0003] However, in many cases, the woody raw material has an immature interior even though its surface appears to be sufficiently ripe, and if the humus portion of the surface layer is first degraded by microorganisms after application to soil. However, the immature wood inside is exposed, and a large amount of nitrogen in the soil is consumed when the wood is decomposed. Therefore, such a wood-based compost has a risk that the soil will cause so-called nitrogen starvation if the application rate is too large. [0004] Woody materials decompose much slower than the decomposition rates of rice husks, rice straw and fallen leaves, which are the organic carbon sources of ordinary compost. For example, it is said that it takes nearly 30 years for soil microorganisms naturally mixed with soil to ripen sufficiently and decompose, so that soil microorganisms no longer require nitrogen. [0005] Under a composting condition in which the temperature is higher than that of the soil, the rate of decomposition of woody materials such as sawdust increases, but it is still necessary to apply the composted woody materials for 3 to 5 months before the nitrogen is not taken up. It takes about two years. By the way, about 5.5 million tons of coal ash is generated annually in Japan due to the operation of thermal power plants.
Fly ash accounts for 0%. Fly ash has been used as an additive to cement in an amount of 50 to 60% of its generation. On the other hand, clinker ash is used not only for civil engineering purposes such as road subgrade materials, but is also directly sprayed directly as an acidic soil improver. [0007] As described above, it is not always preferable to use a wood raw material as an organic carbon source when producing compost in order to produce good compost in a short period of time. However, it was not easy to ripen the raw wood compost in a short period of time without causing nitrogen starvation. [0008] Further, the above-mentioned problems associated with composting of woody materials become particularly apparent when using wood chips such as felled wood chips containing a hardly decomposable wood core. [0009] On the other hand, fly ash and clinker ash, which are a kind of coal ash, are strongly alkaline and, therefore, are limited in the fields where they can be effectively used. [0010] Therefore, an object of the present invention is to solve the above-mentioned problems and to make it possible to produce a sufficiently mature woody compost in a short period of time. Also,
The purpose is to enable effective utilization of coal ash generated by a by-product of a thermal power plant or the like, thereby obtaining a woody raw material compost having a high fertilizer effect. [0011] To solve the above problems BRIEF SUMMARY OF THE INVENTION In the present invention, for the carbon source consisting of chip material 1 m 3, as the water and nitrogen sources poultry 25~50kg
And add 25-150 kg of clinker
And, the mixture can be employed a method of manufacturing a wood raw material compost you humification is fermented in the atmosphere. In the method for producing a woody raw material compost of the present invention,
By admixing coal ash such as click <br/> linker to water and nitrogen source as a carbon source of organic containing wood, 2 0
The nitrate nitrogen content and the carbon ratio of the compost fermented over about one week to thirty weeks can be induced to preferable values, and the desired maturity can be sufficiently advanced. Although the reason why the rate of humification is increased by the addition of coal ash has not yet been sufficiently proved, the inside of the compost can be heated to 60 to 80 ° C., particularly during the initial stage of cellulose decomposition by microbial fermentation. It is considered that the porous coal ash acts like a catalyst at that time, and the decomposition of organic matter by the thermochemical reaction is likely to occur on the surface of the coal ash. In addition, since coal ash exhibits alkalinity, by adding and mixing the same, it is possible to neutralize the organic acid generated by fermentation and adjust the pH of the entire compost raw material to the alkali side, thereby weakening It is also considered that a favorable growth environment for microorganisms that prefer an alkaline environment has been created. Further, woody materials such as wood chips and sawdust have a high carbon content, and it is necessary to add a nitrogen component in order to ripen this. In the above-mentioned method for producing a woody raw material compost, when chicken manure is used as a nitrogen source, not only nitrogen, which tends to be insufficient as a compost component, but also the contents of phosphoric acid and calcium can be sufficiently increased. DETAILED DESCRIPTION OF THE INVENTION organic carbon source comprising wood used in this invention, Chi-up member of any woody or Ranaru organic carbon source
In addition, weeds and other plant matter such as rice hulls, rice straw, bamboo grass, fallen leaves, pampas grass, or organic matter derived from living things such as cattle, horses, pigs, livestock droppings such as chickens, Conventionally usable materials may be used in combination, for example, composting of city garbage. It is preferable that the woody material such as chip material is fiberized using a crusher in order to accelerate the microbial decomposition as quickly as possible. In order to industrially produce such fiberized wood, it is preferable to use a crusher having a crushing function called a tab grinder. The nitrogen source used in the present invention is not particularly limited, and in addition to particularly preferable chicken dung, well-known fertilizers such as urea fertilizer and lime nitrogen fertilizer can be used. The coal ash used in the present invention refers to the ash content of coal, that is, the pyrolysis or oxidation product of coal.
Usually, ash remaining after burning coal. A large amount of coal ash is produced as coal ash waste (clinker ash or fly ash) from thermal power plants, so it is used to effectively utilize resources and provide stable quality soil improvement materials. Is preferred. The clinker (also referred to as clinker) in the present invention is a coal ash that is formed into a lump when coal is calcined, and a portion having a low melting point in the coal is melted and solidified as a whole. , And fly ash. It is preferable to use such a clinker having a particle size of about 5 mm or less in order to uniformly mix and effectively act. The water to be added to the mixture in the present invention is
The amount of water required for the decomposition of organic matter such as microbial fermentation,
An appropriate amount of water is replenished to such an extent that the compost does not dry and water components such as nitrogen and potassium do not flow away. Also, if excess water is present in the compost, the growth of aerobic microorganisms is hindered and the activity of only anaerobic bacteria is activated, so that water squeezed out from the lower part of the compost by the weight of the compost is drained appropriately. It is preferable to use an embanked base, a concrete composter, a basin-shaped drainage stand, or the like. The organic carbon source and coal ash are mixed and hydrated to cause sugar decomposition, cellulose decomposition, and lignin decomposition by natural fermentation. In particular, fermentation heat is generated during the sugar decomposition period and the cellulose decomposition period. . Fermentation heat is generated in the process of decomposing organic materials as raw materials by aerobic microorganisms adhering to the atmosphere, organic carbon sources, and the like. A preferable temperature condition in the compost controlled by using such fermentation heat is about 60 to 80 ° C. This is because a fermentation reaction is slow at a low temperature of less than 60 ° C., and if it is heated to more than 80 ° C., the growth of microorganisms is deteriorated and the fermentation does not proceed. [0025] Incidentally, during the sugar decomposition stage in the early stage of the maturation process of organic substances, relatively easily decomposable substances such as proteins, amino acids, and carbohydrates are decomposed. At this time, aerobic filamentous fungi and bacteria act. I do. Then, in the cellulose decomposition period,
High-temperature aerobic actinomycetes such as Thermoactinomyces, which degrade hemicellulose, and cellulolytic bacteria grow and generate fermentation heat. After that time, the temperature decreases, and lignin is decomposed by basidiomycetes and the like. The wood as a carbon source of organic, click <br/> linker of coal ash, nitrogen source and preferred mixing ratio of the manure of which, in a state where for example the fiber is triturated with a wood was loosened chip In the case of wood, 1 m 3 (about 500 kg if the specific gravity is about 0.5) is
~ 150kg (preferably clinker 25 ~ 150k
g) , a nitrogen source of 5 to 20 kg (preferably urea of 5 to 10 k)
g, lime nitrogen 10-20 kg, chicken dung 25-50 kg). [0027] In a small amount proportion of the coal ash is less than the predetermined range mentioned above, almost no effect of compost maturity accelerated, when a large amount exceeding the predetermined range, water retention becomes poor in click linker, in these cases Is not preferred because it inhibits the growth of microorganisms. If the compounding ratio of the nitrogen source is less than the above-mentioned predetermined range, a shortage of nitrogen constituting the body of microorganisms proliferating at the time of fermentation will be caused, and fermentation will be inferior. When high temperature fermentation continues for a long time in the early stage of fermentation, mineralization of nitrogen content progresses violently,
The nitrogen content taken up by microorganisms does not increase to the same extent,
As a result, a phenomenon in which nitrogen added as a fermentation promoter is released into the atmosphere as ammonia gas and is not effectively used occurs, which is not preferable. Examples and Comparative Examples [Examples 1 to 3, Comparative Examples 1 to
As 6] carbon source, chip material (specific gravity about 0.5) loosened fibers by crushing to grinding the wood waste material in tab grinder, Table 1 nitrogen sources and coal ash (clinker)
And then put it into a composting device of the forced supply and exhaust system (Kawatetsu Shoji Co., Ltd .: Nutrition kun, a device in which a porous pipe connected to a supply and exhaust pump is buried in a cylindrical sheet cladding frame). By adding water so that the water content of the mixed material becomes about 70%, and performing forced aeration every 10 minutes / 3 hours by a supply / exhaust pump to aerobically ferment, the internal temperature of the mixture is reduced for one week. The temperature was kept at 65 to 75 ° C over a period of time. After aerobic fermentation by adjusting the water content and forced aeration so that the internal temperature is 55 to 75 ° C. for 4 to 5 months, it is preferable that the internal temperature drop to 50 to 40 ° C. It was confirmed that the initial fermentation was completed. Thereafter, the compost having been subjected to aerobic fermentation was carried out from the composting apparatus, and was post-ripened for about 2 to 5 months in a piled state to produce compost. [Table 1] The compositions of the clinker ash used in the examples and comparative examples are as follows. Clinker ash: SiO 2 40-75
%, Al 2 O 3 15 to 35%, Fe 2 O 3 2 to 20%,
CaO 1-10%. During the test period of Examples and Comparative Examples in which compost is manufactured under the above conditions, the progress of ripening was examined to
The total carbon content and total nitrogen content were examined by a dry combustion method, the carbon ratio (C / N ratio) was calculated, and the ammonia nitrogen content and nitrate nitrogen content were measured by the Bremner method. Also,
After 10 months, the total amount of phosphorus (P 2 O 5 %) was measured by the quinoline gravimetric method, and the total amount of potassium (K 2 O%) and total calcium (CaO
%) Was measured. Further, a compost sample having a fermentation time of 5, 7 or 10 months was subjected to a seedling test according to a soil culture material test method. The results of these tests are as follows. That is, as is clear from the results shown in the charts of FIGS. 1 and 4, in comparison with the comparative example, the working examples of the present invention showed a higher nitrate nitrogen content (NO 3- N, mg / 100 g). In particular, in Examples 2 and 3, it can be seen that the content of nitrate nitrogen is remarkably increased, and the maturation is rapidly progressing. As is clear from the results shown in FIGS. 2 and 5, the carbon ratio of the Example in the 22nd to 31st weeks was lower than that of the Comparative Example, indicating that You can see that it is progressing. [Table 2] As is clear from the results in Table 2,
In the compost of Example 3 in which coal ash and chicken manure were added in combination,
The contents of phosphorus, potassium and calcium are remarkably high, and it is understood that the use of chicken manure is appropriate for sufficiently supplying these essential components of fertilizer to plants. Next, FIGS. 3 and 6 show the change over time of the PQ value which is known to be able to determine the quality of humus. Here, the PQ value is also referred to as the sediment ratio, as described in Kyoichi Kumada, “Chemistry of Soil Organic Matter”, pp. 124-127.
The ratio (%) of humic acid in the humus extracted using aOH or Na 4 P 2 O 7 as a solvent is a value represented by the following formula. PQ value (%) = [a / (a + b)] × 100 (where a and b are 0.1 N KMnO 4 consumption of humic acid and fulvic acid each corresponding to 1 g of compost (ml)
It is. As is clear from the results shown in FIGS. 3 and 6, the PQ value of Example 1 or Example 3 was lower than that of Comparative Examples 4 to 6 from the 22nd week of the test period. It increased remarkably over the 31st week, indicating that physical properties having high contents of humic acid and fulvic acid useful for growing plants were obtained in a short period of time. Next, in the seedling test, 30 to 70 seedlings of "Sirona" (Brassicaceae) were placed in soil mixed with a certain amount of compost immediately after aerobic fermentation, and 2 or 5 months after laying.
Example 3: Growing for 40 days in a greenhouse controlled at room temperature of 25 ° C. ± 5 ° C. in an environment where watering is appropriately performed without shading.
The growth amount (combined weight of the above-ground part and the root system) of the composts of Comparative Examples 5 and 6 was compared. In order to exclude the influence of the water content, the growth amount was also measured for two weeks under light-shielded conditions and ventilation conditions allowing outside air to enter. In addition, "Sirona" was grown under exactly the same conditions except that the same amount of ordinary compost (without the addition of coal ash) was mixed as a control, and its growth amount (total weight of the above-ground part and root system) Example 3 in a case where is set to 100%
Table 3 shows the biological weights of Comparative Examples 5 and 6. [Table 3] As is clear from the results in Table 3, the biomass weight of the compost of Example 3 having a high PQ value is higher than that of Comparative Examples 5 and 6, and the PQ value is high (63.3 or more). The compost of Example 1 has a high plant growing ability. From these facts, it could be confirmed by the seedling test test that compost having a higher fertilizer effect was produced by adding coal ash to the compost and humifying the compost, as compared with the case where organic matter was simply composted. As described above, the present invention provides a compost in which water, a nitrogen source and coal ash are mixed with an organic carbon source including wood, and this mixture is fermented in the air to produce humus. , The nitrate nitrogen content and carbon ratio of the compost fermented in a relatively short period of about 20 to 30 weeks can be induced to favorable values, which has a favorable effect on plant growth. There is an advantage that a sufficiently mature woody compost can be produced in a short period of time. [0049] In the manufacturing method of the wood raw material compost of the invention, click <br/> linker or Ranaru coal ash large amount generated by-products, such as thermal power plants can be effectively used, thereby resulting fertilizer There is also an advantage that it becomes a highly effective compost. In the above-mentioned method for producing a woody raw material compost, in the invention in which chicken manure is used as the nitrogen source, in addition to the above-mentioned advantages, not only the nitrogen, which tends to be insufficient as a compost component, but also the contents of phosphoric acid and calcium are reduced. There is also an advantage that can be sufficiently increased.

【図面の簡単な説明】 【図1】硝酸態窒素含量と堆肥化期間の関係を示す図表 【図2】炭素率と堆肥化期間の関係を示す図表 【図3】PQ値と堆肥化期間の関係を示す図表 【図4】硝酸態窒素含量と堆肥化期間の関係を示す図表 【図5】炭素率と堆肥化期間の関係を示す図表 【図6】PQ値と堆肥化期間の関係を示す図表[Brief description of the drawings] FIG. 1 is a chart showing the relationship between nitrate nitrogen content and composting period. FIG. 2 is a chart showing a relationship between a carbon ratio and a composting period. FIG. 3 is a chart showing the relationship between PQ value and composting period. FIG. 4 is a table showing the relationship between nitrate nitrogen content and composting period. FIG. 5 is a chart showing the relationship between carbon ratio and composting period. FIG. 6 is a chart showing the relationship between PQ value and composting period.

フロントページの続き (72)発明者 古谷 利夫 大阪市北区中之島3丁目3番22号 関西 電力株式会社内 (72)発明者 杉本 正昭 大阪市北区中之島3丁目3番22号 関西 電力株式会社内 (72)発明者 大塚 紘雄 神戸市灘区六甲台町1番1号 神戸大学 農学部内 (72)発明者 藤嶽 暢英 神戸市灘区六甲台町1番1号 神戸大学 農学部内 (72)発明者 鈴木 武志 神戸市灘区六甲台町1番1号 神戸大学 農学部内 (72)発明者 岡本 昌太郎 神戸市灘区六甲台町1番1号 神戸大学 農学部内 (72)発明者 宇治原 博一 神戸市灘区六甲台町1番1号 神戸大学 農学部内 (56)参考文献 特開 平9−99279(JP,A) 特開 平9−74899(JP,A) 特開 昭51−33071(JP,A) 特開 昭53−109987(JP,A) (58)調査した分野(Int.Cl.7,DB名) C05B 1/00 - C05G 5/00 (72) Inventor Toshio Furuya 3-3-22 Nakanoshima, Kita-ku, Osaka-shi Kansai Electric Power Co., Inc. (72) Inventor Masaaki Sugimoto 3-2-2, Nakanoshima, Kita-ku, Osaka Kansai Electric Power Co., Ltd. (72) Inventor Hiroo Otsuka 1-1, Rokkodai-cho, Nada-ku, Kobe City Inside the Faculty of Agriculture, Kobe University (72) Inventor Nobuhide Fujitake 1-1, Rokkodai-cho, Nada-ku, Kobe City Inside the Faculty of Agriculture, Kobe University (72) Inventor Takeshi Suzuki Kobe 1-1, Rokkodai-cho, Nada-ku, Kobe University Inside of Faculty of Agriculture, Kobe University (72) Inventor Shotaro Okamoto 1-1, Rokkodai-cho, Nada-ku, Kobe City Inside of Faculty of Agriculture, Kobe University (72) Hiroichi Ujihara No. 1, Rokkodai-cho, Nada-ku, Kobe City 1 Kobe University Faculty of Agriculture (56) References JP-A-9-99279 (JP, A) JP-A-9-74899 (JP, A) JP-A-51-33071 (JP, A) JP-A-53-109987 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) C05B 1/00-C05G 5/00

Claims (1)

(57)【特許請求の範囲】 【請求項1】 チップ材1m 3 からなる炭素源に対し
て、水および窒素源として鶏糞25〜50kgを混合
し、さらにクリンカ25〜150kgを添加混合し、
の混合物を大気中で発酵させて腐植化する木質原料堆肥
の製造方法。
(57) Patent Claims 1. A against the carbon source consisting of chip material 1 m 3
Te, mixed manure 25~50kg as water and nitrogen sources
And further the clinker 25~150kg were added and mixed, the mixture method of manufacturing a wood raw material compost you humification is fermented in the atmosphere.
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