JP2909286B2 - Good quality ripening of compost - Google Patents
Good quality ripening of compostInfo
- Publication number
- JP2909286B2 JP2909286B2 JP36152791A JP36152791A JP2909286B2 JP 2909286 B2 JP2909286 B2 JP 2909286B2 JP 36152791 A JP36152791 A JP 36152791A JP 36152791 A JP36152791 A JP 36152791A JP 2909286 B2 JP2909286 B2 JP 2909286B2
- Authority
- JP
- Japan
- Prior art keywords
- compost
- cdu
- fermentation
- added
- ripening
- 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 - Lifetime
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/20—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/145—Feedstock the feedstock being materials of biological origin
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Landscapes
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Biotechnology (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Biochemistry (AREA)
- Tropical Medicine & Parasitology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Organic Chemistry (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Fertilizers (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、堆肥の良質腐熟化法に
関する。更に詳細には、2−オキソ−4−メチル−6−
ウレイドヘキサヒドロピリミジン及び乾血、あるいはこ
れらとともに更に高温好アルカリ性菌を堆肥に添加して
堆肥を良質腐熟化する方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for ripening compost of good quality. More specifically, 2-oxo-4-methyl-6-
The present invention relates to a method of adding ureido hexahydropyrimidine and dry blood, or a high-temperature alkalophilic bacterium to the compost together with the urea hexahydropyrimidine to make the compost good-quality maturation.
【0002】[0002]
【従来の技術】従来から、イナワラ、麦ワラなどからな
る堆肥は、田畑の土壌の物理性、化学性及び生物性を改
善し作物の安定増収と土壌の肥沃化に効果を有する事が
知られており、農家では通常いわゆる土づくりのために
堆肥の施用が行われている。現在では、イナワラ、麦ワ
ラ、バーク鋸屑、家畜糞尿などの各種材料を利用して機
械的に堆肥化する技術はある程度確立されている。2. Description of the Related Art It has been known that compost comprising rice straw, wheat straw and the like has been known to improve the physical properties, chemical properties and biological properties of field soil, and to stably increase crop yield and fertilize the soil. Farmers usually apply compost to make soil. At present, a technique of mechanically composting using various materials such as rice straw, wheat straw, bark sawdust, and livestock manure has been established to some extent.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、微生物
を利用した堆肥の良質腐熟化についての研究については
殆どなされておらず、また各種肥料と堆肥の良質腐熟化
との関係についての詳細な研究も行われていない。However, there has been little research on the good quality maturation of compost using microorganisms, and detailed research on the relationship between various fertilizers and good quality maturation of compost has been conducted. Not done.
【0004】[0004]
【課題を解決するための手段】本発明者らは、堆肥の発
酵はアルカリ性で進行することから好アルカリ性微生物
の関与について着目し、好アルカリ性微生物を利用した
堆肥の良質腐熟化について研究を行った。また各種肥料
が堆肥の良質腐熟化に及ぼす影響について研究を行っ
た。その結果、緩効性窒素肥料として知られる2−オキ
ソ−4−メチル−6−ウレイドヘキサヒドロピリミジン
及び乾血、あるいはこれらとともに更に高温好アルカリ
性菌を堆肥に添加して発酵させることにより堆肥を良質
腐熟化させることができることを見出し本発明を完成さ
せた。Means for Solving the Problems The present inventors have paid attention to the involvement of alkalophilic microorganisms since fermentation of compost proceeds in an alkaline manner, and studied on good quality maturation of compost using alkalophilic microorganisms. . We also studied the effects of various fertilizers on the maturity of compost. As a result, 2-oxo-4-methyl-6-ureidohexahydropyrimidine and dry blood, which are known as slow-release nitrogen fertilizers, or dry blood, or a high-temperature alkalophilic bacterium is further added to the compost to ferment the compost, thereby improving the quality of the compost. It has been found that ripening can be achieved, and the present invention has been completed.
【0005】即ち、本発明は、堆肥に、2−オキソ−4
−メチル−6−ウレイドヘキサヒドロピリミジン及ひ乾
血、あるいはこれらとともに高温好アルカリ性菌を添加
して発酵させることを特徴とする堆肥の良質腐熟化法で
ある。That is, the present invention relates to a method for producing 2-oxo-4
-Methyl-6-ureidohexahydropyrimidine and dry blood, or a fermentation method by adding a high-temperature alkalophilic bacterium and fermentation together with them to ferment the compost.
【0006】本発明で対象とする堆肥は、当業者におい
て通常知られているいずれの堆肥でもよく、通常、イナ
ワラ、麦ワラ、バーク鋸屑、家畜糞尿などの各種材料を
自然堆積しあるいは機械的処理して常法により得られる
堆肥である。堆肥に添加する2−オキソ−4−メチル−
6−ウレイドヘキサヒドロピリミジンは、緩効性窒素肥
料として広く使用されているものであり、分子量172
の非吸湿性のウレイド化合物の1種であり、市販品のも
のをそのまま用いることができる。2−オキソ−4−メ
チル−6−ウレイドヘキサヒドロピリミジンの堆肥への
添加量は通常1.0〜3.0重量%、好ましくは2.0
〜2.5重量%である。添加時期は、特に制限はなくい
ずれでもよいが、例えば、堆肥として自然堆積する最初
の時期、あるいは自然堆積後数ケ月から数年後に添加す
ることができる。堆肥を機械的に製造する場合にも同様
に最初の時期あるいは製造後発酵させて数ケ月から数年
後に添加することができる。[0006] The compost to be used in the present invention may be any compost generally known to those skilled in the art. Usually, various materials such as rice straw, wheat straw, bark sawdust and livestock manure are naturally deposited or mechanically treated. This is compost obtained by conventional methods. 2-oxo-4-methyl-added to compost
6-Ureidohexahydropyrimidine is widely used as a slow-release nitrogen fertilizer and has a molecular weight of 172.
Is a non-hygroscopic ureide compound, and a commercially available product can be used as it is. The amount of 2-oxo-4-methyl-6-ureidohexahydropyrimidine added to compost is usually 1.0 to 3.0% by weight, preferably 2.0%.
~ 2.5% by weight. The addition time is not particularly limited, and may be any time. For example, it can be added at the first time of natural deposition as compost, or several months to several years after natural deposition. Similarly, when compost is produced mechanically, it can be added at the initial stage or after several months to several years after fermentation after production.
【0007】2−オキソ−4−メチル−6−ウレイドヘ
キサヒドロピリミジンとともに用いる乾血も、通常、窒
素肥料としてよく使用されるものであり、いずれの種類
のものを用いてもよく、例えば動物性タンパク質窒素乾
血などを例示することができる。乾血の堆肥への添加量
は通常1.5〜3.5重量%、好ましくは1.5〜1.
8重量%である。添加時期は2−オキソ−4−メチル−
6−ウレイドヘキヒドロピリミジンの場合と同様であ
り、これと一緒にあるいは別の時期に添加してもよい。[0007] Dry blood used together with 2-oxo-4-methyl-6-ureidohexahydropyrimidine is also commonly used as a nitrogen fertilizer, and any type may be used. Protein nitrogen dry blood and the like can be exemplified. The amount of dry blood added to compost is usually 1.5 to 3.5% by weight, preferably 1.5 to 1.
8% by weight. The time of addition is 2-oxo-4-methyl-
As in the case of 6-ureidohexyhydropyrimidine, it may be added together or at another time.
【0008】堆肥に2−オキソ−4−メチル−6−ウレ
イドヘキサヒドロピリミジンと乾血を添加することによ
って、得られる堆肥を作物の土壌に適用した場合、作物
の幼苗の生育を促進する効果を奏する。また、作物の病
害防除に有効であり、特にキュウリつる割病などの防除
に有効である。更には、堆肥の腐熟化の進み具合いの指
標となる炭素/窒素比、塩基置換容量(CEC)、腐植
酸含量の数値を改善し得る効果も奏する。また、堆肥の
発酵に深く関与すると考えられる堆肥中の高温性微生物
の菌数を増加させる効果も奏する。[0008] By adding 2-oxo-4-methyl-6-ureidohexahydropyrimidine and dry blood to compost, when the resulting compost is applied to the soil of a crop, the effect of promoting the growth of seedlings of the crop is improved. Play. In addition, it is effective for controlling disease of crops, and particularly effective for controlling cucumber vine disease. Furthermore, the present invention has the effect of improving the values of the carbon / nitrogen ratio, base substitution capacity (CEC), and humic acid content, which are indicators of the progress of maturation of compost. In addition, an effect of increasing the number of thermophilic microorganisms in the compost which is considered to be deeply involved in the fermentation of the compost is also exerted.
【0009】本発明では、2−オキソ−4−メチル−6
−ウレイドヘキサヒドロピリミジン及び乾血とともに高
温好アルカ性菌を添加してもよい。このような菌として
はBacillus属に属する菌が挙げられ、例えばB
acillus licheniformis(IFO
−14026)などが例示される。これらの菌の実際に
添加する場合には、菌の培養液を堆肥に添加する。菌の
添加量は通常、培養液として5〜20容量%、好ましく
は10〜20容量%である。菌の添加時期は、2−オキ
ソ−4−メチル−6−ウレイドヘキサヒドロピリミジン
あるいは乾血の場合と同様である。菌を添加することに
よって、得られる堆肥を作物の土壌に適用した場合に、
作物の病害防除、特にキュウリつる割病の防除に有効で
ある。また他の面においても堆肥の腐熟化に良好な結果
をもたらすことができる。In the present invention, 2-oxo-4-methyl-6 is used.
-Thermophilic alkalophilic bacteria may be added together with ureido hexahydropyrimidine and dry blood. Examples of such bacteria include bacteria belonging to the genus Bacillus.
acillus licheniformis (IFO
-14026). When actually adding these fungi, a culture solution of the fungi is added to the compost. The addition amount of the bacterium is usually 5 to 20% by volume, preferably 10 to 20% by volume as a culture solution. The time of addition of the bacteria is the same as in the case of 2-oxo-4-methyl-6-ureidohexahydropyrimidine or dry blood. When the resulting compost is applied to crop soil by adding fungi,
It is effective for controlling disease of crops, especially controlling cucumber vine disease. In other aspects, good results can be obtained in the maturation of compost.
【0010】以上に詳述した窒素肥料あるいは高温好ア
ルカリ性菌を添加して堆肥を発酵させるには、そのまま
数ケ月間〜数年間、通常の方法で自然堆積しておけばよ
い。あるいは発酵層に堆積して発酵させてもよい。In order to ferment the compost by adding the nitrogen fertilizer or the high-temperature alkalophilic bacterium described in detail above, the compost may be naturally deposited for a few months to several years by a usual method. Alternatively, the fermentation may be performed by depositing on a fermentation layer.
【0011】[0011]
【発明の効果】かくして、本発明によれば、堆肥の良質
腐熟化を行うことができる。本発明によって得られる堆
肥を作物に適用した場合には、幼苗の生育を促進し、ま
たキュウリつる割病などの病害を有効に防除することも
達成でき、農業等に及ぼす意義は極めて深い。As described above, according to the present invention, the compost can be ripened with good quality. When the compost obtained according to the present invention is applied to crops, it can promote the growth of seedlings and can effectively control diseases such as cucumber vine wilt, and its significance to agriculture and the like is extremely deep.
【0012】[0012]
【実施例】以下、本発明を実施例により更に詳細に説明
する。 実施例 <堆肥の腐熟化> A.合成有機質緩効性窒素肥料である2−オキソ−4−
メチル−6−ウレイドヘキサヒドロピリミジン(以下C
DUと略記する)と、CDUに動物性タンパク質窒素乾
血を混合した窒素源の、バークの腐熟化に及ぼす影響1
年間自然堆積したソビエトカラマツのバーク堆肥2Kg
(含水率67%)に窒素源として、CDU55.5
g、鶏ふん34g、CDU44.5g、乾血34g、
鶏ふん34g、鶏ふん34gを添加した。なお、窒素
源以外には、過りん酸石灰を20g、米ぬか20gを添
加した。これらのバークは直径30cm、深さ12cm
のホーロー缶に入れて蓋をし、50℃のインキュベータ
内で2ケ月間発酵させた。The present invention will be described in more detail with reference to the following examples. Example <Maturation of compost> Synthetic organic slow-release nitrogen fertilizer 2-oxo-4-
Methyl-6-ureidohexahydropyrimidine (hereinafter referred to as C
DU) and animal protein nitrogen dry
Effect of nitrogen source mixed with blood on ripening of bark 1
2kg of bark compost of Soviet larch naturally deposited every year
(Water content 67%), as a nitrogen source, CDU55.5
g, chicken feces 34 g, CDU 44.5 g, dry blood 34 g,
34 g of chicken dung and 34 g of chicken dung were added. In addition to the nitrogen source, 20 g of lime superphosphate and 20 g of rice bran were added. These barks are 30cm in diameter and 12cm deep
Was put in an enamel can, covered, and fermented in a 50 ° C. incubator for 2 months.
【0013】B.Aの処理に高温好アルカリ性菌Bac
illus licheniformis(IFO−1
4026)を添加した場合の、バーク堆肥の腐熟化に対
する影響Aのの処理にB.licheniform
isの振とう培養液を350ml添加した。対照区(鶏
糞のみの区)は水を350ml添加した。発酵の処理方
法はAと同じである。 C.中規模発酵テスト 1年間自然堆積したソビエトカラマツのバーク堆肥7ト
ンにCDU156Kg、乾血119Kg、乾燥鶏糞
1,500Kgを窒素源として添加した。窒素源以外
に、過りん酸石灰と米ぬかを70Kgずつ添加した。こ
れらのバークはシャベル車でよく混合し、間口3.5
m、奥行き3.0mの発酵層に堆積し発酵を行った。 <試験方法> (1)腐熟化の過程でpH、EC、CEC及び高温性微
生物の菌数を以下に示す方法により調べた。 a)、pH及びECは各々のメーターを用いて測定し
た。 b)、CEC:セミミクロショーレンベルジャー法で行
った。 c)、高温性微生物の菌数:微生物の分離は希釈平板法
で行った。また、堆肥は深さ40cmより採取したサン
プルを用い、培養温度は28℃と50℃とした。B. A high-temperature alkalophilic bacterium Bac
illus licheniformis (IFO-1
4026) against the ripening of bark compost
B. to the processing of the impact A to licheniform
350 ml of the shaking culture of is was added. In the control section (section only with chicken dung), 350 ml of water was added. The method of fermentation is the same as A. C. Medium-scale fermentation test To 7 tons of bark compost of Soviet larch naturally deposited for one year, 156 kg of CDU, 119 kg of dry blood, and 1,500 kg of dried chicken manure were added as nitrogen sources. In addition to the nitrogen source, 70 kg of lime superphosphate and rice bran were added. These barks are mixed well with a shovel and have a frontage of 3.5
m, a fermentation layer having a depth of 3.0 m was fermented. <Test method> (1) pH, EC, CEC, and the number of thermophilic microorganisms were examined in the course of ripening by the following method. a), pH and EC were measured using each meter. b), CEC: Performed by the semi-micro Schöllenberger method. c) Number of thermophilic microorganisms: Microorganisms were separated by a dilution plate method. The compost used was a sample collected from a depth of 40 cm, and the culture temperatures were 28 ° C. and 50 ° C.
【0014】(2)キュウリ幼苗の生育に及ぼす影響を
調査した。 洪積層土壌(N:P:K=0.013:0.031:
0.056%、CEC=4.76me/100g)1リ
ットル当り供試堆肥を50g混合して直径15cmの素
焼鉢に詰め、1ポット当り10粒のキュウリを播種し
た。肥料は高橋培土試剤検定法に従って、N、P、Kを
それぞれ土壌1リットル当り100mg使用した。調査
は播種後30日に行い、各区10ポットの3反復行っ
た。 (3)発酵バーク堆肥のキュウリつる割病の発生に及ぼ
す影響を調べた。洪積層土壌5リットリ当りに、振とう
培養したキュウリつる割病菌を200ml接種し、60
日後この汚染土壌1リットルに対し供試堆肥を50g混
合し、直径15cmの素焼鉢につめた。この素焼鉢1ポ
ット当りにキュウリ(品種:青長四葉)種子を10粒ず
つ播種し、萎凋枯死個体数を調べて発病率とした。実験
は各区5ポット用い、時期をずらして3反復行った堆肥
施用土壌はN、P、Kをそれぞれ100mg/リットル
(土壌)使用した。一方、CDUの発酵効果を調べるた
め、窒素無添加発酵堆肥施用土壌に、化成肥料の替わり
に窒素成分か100mg/リットル(土壌)になるよう
CDUを加えた。また化成肥料とCDUの病気発生に及
ぼす影響を調べるために汚染土壌で両者を比較した。 (4)C/NはNCアナライザー(スミグラフNC−8
0型)で測定した。 (5)アンモニウム態窒素は塩化カリウム液浸出法で測
定した。(2) The influence on the growth of cucumber seedlings was investigated. Flood-stacked soil (N: P: K = 0.013: 0.031:
(0.056%, CEC = 4.76me / 100g) 50 g of the test compost was mixed per liter and packed in a clay pot having a diameter of 15 cm, and 10 cucumber seeds were sown per pot. The fertilizer used was 100 mg of N, P, and K per liter of soil according to the Takahashi soil test method. The survey was performed 30 days after sowing, and three repetitions of 10 pots in each section were performed. (3) The effect of fermented bark compost on the occurrence of cucumber wilt was investigated. Inoculation of 200 ml of cucumber vine wilt fungus cultured with shaking per 5 liters of flood-laden soil was performed.
One day later, 1 g of this contaminated soil was mixed with 50 g of test compost and filled in a clay pot having a diameter of 15 cm. 10 seeds of cucumber (cultivar: blue long four-leaf) seeds were sowed per pot of this unglazed pot and the number of withered and dead individuals was checked to determine the disease incidence. In the experiment, five pots were used for each section, and N, P, and K were each used at 100 mg / liter (soil) for compost application soil that was repeated three times at different times. On the other hand, in order to examine the fermentation effect of CDU, CDU was added to the nitrogen-added fermentation compost applied soil in place of the chemical fertilizer so that the nitrogen content was 100 mg / liter (soil). In order to examine the effects of chemical fertilizer and CDU on disease outbreak, the two were compared in contaminated soil. (4) C / N is an NC analyzer (Sumigraph NC-8)
0). (5) Ammonium nitrogen was measured by a potassium chloride leaching method.
【0015】<試験結果> (1)pH、EC及びCECの変動 A、B及びCの方法でそれぞれ腐熟化した場合のpHと
EC変動をそれぞれ図1、図2及び図3に示した。CE
Cの変動はそれぞれ図4、図5及び図6に示した。Aの
方法で腐熟化した場合、pHとECの変動については対
照区の堆肥が最も低く、CDUと乾血を窒素源にした堆
肥が最も高かった。CECについては発酵1ケ月目迄は
ほとんど同じであったが、2ケ月目には明らかに差が認
められ、CDUと乾血を窒素源にした堆肥が最も高かっ
た。Bの場合、発酵日数に伴うpH、EC及びCECの
推移は、Aと同じ傾向を示しB.lichenifor
misの添加による変化はあまりなかった。Cの場合、
pH及びECの変動は、鶏糞をバークに混合するとpH
はすぐに上昇し、その後は中性に保っていた。CDUの
添加はバークのpHの急激な上昇に影響を与えないが、
発酵1ケ月目のpHは中性で、2ケ月目の堆肥は弱酸性
であった。一方、ECは鶏糞添加バーク堆肥の方が高
く、1.7〜1.9ms/cmの間で変動し、CDU添
加バーク堆肥は発酵日数に伴って上昇傾向を示し、2ケ
月目のバーク堆肥は1.3ms/cmであった。CEC
については、CDUを窒素源にしたバーク堆肥の方が高
かった。<Test Results> (1) Fluctuations in pH, EC and CEC The fluctuations in pH and EC when ripened by the methods A, B and C are shown in FIGS. 1, 2 and 3, respectively. CE
The variation of C is shown in FIGS. 4, 5 and 6, respectively. In the case of ripening by the method of A, the fluctuation in pH and EC was the lowest in the control compost, and the highest in the compost using CDU and dry blood as the nitrogen source. The CEC was almost the same up to the first month of fermentation, but the difference was clearly observed at the second month, with the highest compost using CDU and dry blood as the nitrogen source. In the case of B, the changes in pH, EC and CEC with the number of fermentation days show the same tendency as A, and B. lichenifor
There was little change due to the addition of mis. In the case of C,
Variations in pH and EC were caused by mixing chicken dung with bark.
Rose quickly and remained neutral thereafter. The addition of CDU does not affect the sharp rise in bark pH,
The pH in the first month of fermentation was neutral, and the compost in the second month was weakly acidic. On the other hand, EC was higher in chicken manure-added bark compost, and fluctuated between 1.7 to 1.9 ms / cm, and CDU-added bark compost showed a tendency to increase with the number of fermentation days. 1.3 ms / cm. CEC
For bark compost using CDU as a nitrogen source, the value was higher.
【0016】(2)高温微生物の菌数の推移 A,B及びCの方法でそれぞれ腐熟化した場合の高温微
生物の菌数の推移をそれぞれ図7,図8及び図9に示し
た。Aの場合、高温性細菌と放線菌は発酵の日数に従っ
て増加したが、糸状菌は減少する傾向を示した。また、
細菌と放線菌の菌数はCDU+乾血>CDU>対照区の
順であった。Bの場合、発酵に伴う高温微生物の推移も
Aと同じ傾向を示した。また、B.lichenifo
rmisの添加による細菌数の増加はなかった。Cの場
合、高温微生物の菌数の変動は、糸状菌は鶏糞添加バー
ク堆肥で多く検出され、放線菌及び細菌は逆にCDU添
加バーク堆肥で多く検出された。(2) Changes in the Number of Bacteria of High-Temperature Microorganisms Changes in the number of bacteria of high-temperature microorganisms when ripened by the methods A, B and C are shown in FIGS. 7, 8 and 9, respectively. In case A, thermophilic bacteria and actinomycetes increased according to the number of days of fermentation, while filamentous fungi showed a tendency to decrease. Also,
The numbers of bacteria and actinomycetes were CDU + dry blood>CDU> control. In the case of B, the transition of the high temperature microorganisms accompanying the fermentation also showed the same tendency as in the case of A. B. lichenifo
There was no increase in the bacterial count with the addition of rmis. In the case of C, the change in the bacterial count of the high-temperature microorganisms was that filamentous fungi were often detected in bark compost with chicken dung, and actinomycetes and bacteria were detected in bark compost with CDU.
【0017】(3)キュウリ幼苗の生育に及ぼす影響 A及びBの方法でそれぞれ腐熟化した場合の影響を、そ
れぞれ図10及び図11に示した。Aの場合、葉数、草
丈、地上部乾重及び根の乾重を調べたが、いずれもCD
U+乾血発酵堆肥が最も優れており、次はCDU区で、
対照区の順であった。Bの場合、Aの結果と同じCDU
+乾血>CDU>対照区の順で優れていた。B.lic
heniformisの添加による効果はあまり認めら
れなかった。(3) Effect on growth of cucumber seedlings The effects of ripening by the methods A and B are shown in FIGS. 10 and 11, respectively. In the case of A, leaf number, plant height, above-ground dry weight and root dry weight were examined.
U + dry blood fermentation compost is the best, next is CDU section.
The order of the control group was as follows. In the case of B, the same CDU as the result of A
+ Dry blood>CDU> Control was better in this order. B. lic
The effect of the addition of C. heniformis was not significantly observed.
【0018】(4)キュウリつる割病の発生に及ぼす影
響 A及びBの方法でそれぞれ腐熟化した場合の影響を、A
及びBの場合の結果を図12、Cの場合の結果を図13
に示した。A及びBの場合、キュウリつる割病の発生に
及ぼす影響については、CDU等窒素源を添加して発酵
した堆肥を使用した区において、発病の軽減効果が認め
られた。B.licheniformisの添加処理堆
肥は無処理堆肥よりも発病がやや少なくなる傾向を示し
た。一方、発酵後の堆肥にCDUを添加した場合は、C
DUを添加して発酵した堆肥に比べて発病が激しく、大
きな軽減効果が認められなかったが、化成肥料使用に比
べると発病は少なかった。また、汚染土壌で化成肥料と
CDUの発病に及ぼす影響を調べても、CDUの方が明
らかに発病が少なかった。Cの場合、キュウリつる割病
の発病に及ぼす影響については、CDUで発酵した堆肥
を使用した区において著しい軽減効果が認められた。鶏
糞で発酵した堆肥を使用した区は、堆肥無施用区に比べ
て発病の軽減が認められたが、CDU堆肥よりはるかに
劣っていた。(4) Influence on the occurrence of cucumber wilt disease The effects of ripening by methods A and B, respectively, are as follows:
12 and FIG. 13 show the results in the case of FIG.
It was shown to. In the case of A and B, as for the effect on the occurrence of cucumber wilt, in the plot using a compost fermented by adding a nitrogen source such as CDU, the effect of reducing the disease was observed. B. The compost treated with L. licheniformis tended to be slightly less sick than the untreated compost. On the other hand, when CDU is added to the compost after fermentation, C
The disease was more intense than compost fermented by adding DU, and no significant reduction effect was observed. However, the disease was less intense than the use of chemical fertilizer. In addition, when examining the effects of chemical fertilizers and CDU on the pathogenesis in contaminated soil, CDU was clearly lower in pathogenesis. In the case of C, a remarkable reduction effect on the onset of cucumber wilt was observed in the plot using compost fermented with CDU. The plot using the compost fermented with chicken manure showed a reduction in the incidence of disease compared to the plot without compost, but was much inferior to the CDU compost.
【0019】 (5)C/N及びアンモニウム態窒素の変動 Cの方法で腐熟化した場合のC/N及びアンモニウム態
窒素の変動を表1に示した。(5) Fluctuation of C / N and ammonium nitrogen The fluctuation of C / N and ammonium nitrogen when ripened by the method of C is shown in Table 1.
【表1】 [Table 1]
【0020】表1から判るように、全炭素は発酵の日数
に伴って減少するようで、全窒素はその逆であった。ま
た、アンモニウム態窒素は全窒素と同様、発酵の経過日
数に従って増加した。As can be seen from Table 1, total carbon seemed to decrease with the number of days of fermentation, and total nitrogen was vice versa. In addition, ammonium nitrogen increased in accordance with the number of days of fermentation similarly to total nitrogen.
【図1】実施例に記載したAの方法で腐熟化した時のp
HとEC変動を示す。BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 shows p when matured by the method A described in Examples.
H and EC fluctuations are shown.
【図2】Bの方法で腐熟化した時のpHとECの変動を
示す。FIG. 2 shows changes in pH and EC when ripened by the method of B.
【図3】Cの方法で腐熟化した時のpHとECの変動を
示す。FIG. 3 shows changes in pH and EC when ripened by the method of C.
【図4】Aの方法で腐熟化した時のCECの変動を示
す。FIG. 4 shows the variation of CEC when ripened by the method of A.
【図5】Bの方法で腐熟化した時のCECの変動を示
す。FIG. 5 shows the variation of CEC when ripened by the method of B.
【図6】Cの方法で腐熟化した時のCECの変動を示
す。FIG. 6 shows the variation of CEC when ripened by the method of C.
【図7】Aの方法で腐熟化した時の高温微生物の菌数の
推移を示す。FIG. 7 shows changes in the number of high-temperature microorganisms when ripened by the method A.
【図8】Bの方法で腐熟化した時の高温微生物の菌数の
推移を示す。FIG. 8 shows the change in the number of high-temperature microorganisms when ripened by the method of B.
【図9】Cの方法で腐熟化した時の高温微生物の菌数の
推移を示す。FIG. 9 shows the change in the number of high-temperature microorganisms when ripened by the method C.
【図10】Aの方法で腐熟化した時のキュウリ幼苗の生
育に及ぼす影響を示す。FIG. 10 shows the effect on the growth of cucumber seedlings when ripened by the method of A.
【図11】Bの方法で腐熟化した時のキュウリ幼苗の生
育に及ぼす影響を示す。FIG. 11 shows the effect of ripening by the method of B on the growth of cucumber seedlings.
【図12】A及びBの方法で腐熟化した時のキュウリつ
る割病の発生に及ぼす影響を示す。FIG. 12 shows the effect of ripening by methods A and B on the occurrence of cucumber wilt.
【図13】Cの方法で腐熟化した時のキュウリつる割病
の発生に及ぼす影響を示す。FIG. 13 shows the effect of ripening by the method C on the occurrence of cucumber wilt.
Claims (3)
ウレイドヘキサヒドロピリミジン及び乾血を添加して発
酵させることを特徴とする堆肥の良質腐熟化法。(1) 2-oxo-4-methyl-6 is added to compost.
A method for ripening compost of good quality, comprising fermenting ureido hexahydropyrimidine and dry blood.
ヘキサヒドロピリミジン及び乾血とともに、高温好アル
カリ性菌を添加する請求項1記載の堆肥の良質腐熟化
法。2. The method of claim 1, wherein a high-temperature alkalophilic bacterium is added together with 2-oxo-4-methyl-6-ureidohexahydropyrimidine and dry blood.
licheniformisである請求項2記載の堆
肥の良質腐熟化法。3. The method according to claim 1, wherein the thermophilic alkalophilic bacterium is Bacillus.
3. The method for ripening compost of good quality according to claim 2, which is L. licheniformis .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP36152791A JP2909286B2 (en) | 1991-12-27 | 1991-12-27 | Good quality ripening of compost |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP36152791A JP2909286B2 (en) | 1991-12-27 | 1991-12-27 | Good quality ripening of compost |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH06100392A JPH06100392A (en) | 1994-04-12 |
| JP2909286B2 true JP2909286B2 (en) | 1999-06-23 |
Family
ID=18473941
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP36152791A Expired - Lifetime JP2909286B2 (en) | 1991-12-27 | 1991-12-27 | Good quality ripening of compost |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2909286B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1996019420A1 (en) * | 1994-12-20 | 1996-06-27 | Mitsuyo Kimura | Fermentation product and process for producing the same |
-
1991
- 1991-12-27 JP JP36152791A patent/JP2909286B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH06100392A (en) | 1994-04-12 |
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