JPH02265700A - Recovery of calcium compound from putrefactive waste - Google Patents
Recovery of calcium compound from putrefactive wasteInfo
- Publication number
- JPH02265700A JPH02265700A JP1087744A JP8774489A JPH02265700A JP H02265700 A JPH02265700 A JP H02265700A JP 1087744 A JP1087744 A JP 1087744A JP 8774489 A JP8774489 A JP 8774489A JP H02265700 A JPH02265700 A JP H02265700A
- Authority
- JP
- Japan
- Prior art keywords
- waste
- calcium
- combustion
- putrescible
- recovering
- 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
- 239000002699 waste material Substances 0.000 title claims abstract description 32
- 229940043430 calcium compound Drugs 0.000 title claims abstract description 22
- 150000001674 calcium compounds Chemical class 0.000 title claims abstract description 22
- 238000011084 recovery Methods 0.000 title 1
- 238000002485 combustion reaction Methods 0.000 claims abstract description 27
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims abstract description 23
- 238000000034 method Methods 0.000 claims abstract description 21
- 239000000654 additive Substances 0.000 claims abstract description 20
- 239000000126 substance Substances 0.000 claims abstract description 20
- 239000002002 slurry Substances 0.000 claims abstract description 19
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 claims abstract description 16
- 230000000996 additive effect Effects 0.000 claims abstract description 16
- 239000000292 calcium oxide Substances 0.000 claims abstract description 14
- 235000012255 calcium oxide Nutrition 0.000 claims abstract description 14
- 239000001506 calcium phosphate Substances 0.000 claims abstract description 11
- 229910000389 calcium phosphate Inorganic materials 0.000 claims abstract description 11
- 235000011010 calcium phosphates Nutrition 0.000 claims abstract description 11
- QORWJWZARLRLPR-UHFFFAOYSA-H tricalcium bis(phosphate) Chemical compound [Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O QORWJWZARLRLPR-UHFFFAOYSA-H 0.000 claims abstract description 11
- 229910000019 calcium carbonate Inorganic materials 0.000 claims abstract description 8
- 239000000203 mixture Substances 0.000 claims abstract description 7
- 238000003756 stirring Methods 0.000 claims abstract description 6
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims abstract description 5
- 239000007788 liquid Substances 0.000 claims abstract description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 22
- 239000000376 reactant Substances 0.000 claims description 12
- 238000006243 chemical reaction Methods 0.000 claims description 11
- 238000001035 drying Methods 0.000 claims description 10
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 6
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims description 5
- 239000001569 carbon dioxide Substances 0.000 claims description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 3
- 239000010800 human waste Substances 0.000 claims description 3
- 239000000395 magnesium oxide Substances 0.000 claims description 3
- 230000008635 plant growth Effects 0.000 claims description 2
- 239000006185 dispersion Substances 0.000 claims 1
- 238000000855 fermentation Methods 0.000 claims 1
- 230000004151 fermentation Effects 0.000 claims 1
- 244000144972 livestock Species 0.000 claims 1
- 238000002156 mixing Methods 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 4
- 238000009264 composting Methods 0.000 abstract description 3
- 241001465754 Metazoa Species 0.000 abstract description 2
- 230000029142 excretion Effects 0.000 abstract 1
- 238000009332 manuring Methods 0.000 abstract 1
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 30
- 239000007795 chemical reaction product Substances 0.000 description 24
- 239000003337 fertilizer Substances 0.000 description 19
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 15
- 239000002994 raw material Substances 0.000 description 12
- 239000010871 livestock manure Substances 0.000 description 11
- 210000003608 fece Anatomy 0.000 description 8
- 239000000463 material Substances 0.000 description 8
- 241000287828 Gallus gallus Species 0.000 description 7
- 235000013330 chicken meat Nutrition 0.000 description 7
- 239000002689 soil Substances 0.000 description 7
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 6
- 239000000920 calcium hydroxide Substances 0.000 description 6
- 235000011116 calcium hydroxide Nutrition 0.000 description 6
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 6
- 230000000052 comparative effect Effects 0.000 description 5
- 239000007789 gas Substances 0.000 description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- 238000003306 harvesting Methods 0.000 description 4
- 150000002632 lipids Chemical class 0.000 description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 3
- 241000196324 Embryophyta Species 0.000 description 3
- 229910052791 calcium Inorganic materials 0.000 description 3
- 239000011575 calcium Substances 0.000 description 3
- 239000010849 combustible waste Substances 0.000 description 3
- 239000003921 oil Substances 0.000 description 3
- 150000003904 phospholipids Chemical class 0.000 description 3
- 239000012066 reaction slurry Substances 0.000 description 3
- 239000010801 sewage sludge Substances 0.000 description 3
- 240000002234 Allium sativum Species 0.000 description 2
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 235000004611 garlic Nutrition 0.000 description 2
- 238000006703 hydration reaction Methods 0.000 description 2
- 239000002440 industrial waste Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 235000019645 odor Nutrition 0.000 description 2
- 244000144977 poultry Species 0.000 description 2
- 235000013594 poultry meat Nutrition 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- 239000002023 wood Substances 0.000 description 2
- 240000005528 Arctium lappa Species 0.000 description 1
- 235000003130 Arctium lappa Nutrition 0.000 description 1
- 235000008078 Arctium minus Nutrition 0.000 description 1
- 241000283690 Bos taurus Species 0.000 description 1
- 241001510071 Pyrrhocoridae Species 0.000 description 1
- 244000061458 Solanum melongena Species 0.000 description 1
- 235000002597 Solanum melongena Nutrition 0.000 description 1
- 244000300264 Spinacia oleracea Species 0.000 description 1
- 235000009337 Spinacia oleracea Nutrition 0.000 description 1
- 241000282887 Suidae Species 0.000 description 1
- 241000607479 Yersinia pestis Species 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000008280 blood Substances 0.000 description 1
- 210000004369 blood Anatomy 0.000 description 1
- 235000010216 calcium carbonate Nutrition 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 235000014113 dietary fatty acids Nutrition 0.000 description 1
- 239000000194 fatty acid Substances 0.000 description 1
- 229930195729 fatty acid Natural products 0.000 description 1
- 150000004665 fatty acids Chemical class 0.000 description 1
- 230000004720 fertilization Effects 0.000 description 1
- -1 for example Substances 0.000 description 1
- 125000005456 glyceride group Chemical group 0.000 description 1
- 230000012010 growth Effects 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 238000004898 kneading Methods 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 230000005923 long-lasting effect Effects 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 230000002085 persistent effect Effects 0.000 description 1
- 238000005554 pickling Methods 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 235000020083 shōchū Nutrition 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 239000003516 soil conditioner Substances 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Landscapes
- Treatment Of Sludge (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は、家畜糞尿、−上下水余剰汚泥その他の腐敗性
廃棄物を処理し、この腐敗性廃棄物からカルシウム化合
物を回収するため方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to a method for treating livestock manure, water/sewage surplus sludge and other putrescible wastes and recovering calcium compounds from the putrescible wastes. It is something.
(従来の技術とその問題点)
腐敗性廃棄物のうち、例えば、牛、豚、鶏などの家畜糞
尿は、オガ屑あるいはバークに含浸させ、これを醗酵さ
せて堆肥化させることによりその処理を図っている。(Prior art and its problems) Among putrescible wastes, for example, livestock manure from cows, pigs, chickens, etc. can be treated by impregnating sawdust or bark, and fermenting and composting this. I'm trying.
また、上下水余剰汚泥などは堆肥化、埋立、燃焼など種
々の処理法が採用されている。In addition, various treatment methods such as composting, landfilling, and combustion are used to treat surplus water and sewage sludge.
更に、一部の腐敗性産業廃棄物にいたっては、消石灰な
どを添加して固化し、そのまま所定の場所に投棄してい
るにすぎないのが現状である。Furthermore, the current situation is that some putrescible industrial waste is simply solidified by adding slaked lime and the like, and then dumped as is in a designated location.
従って、この種の廃棄物を処理するにあたっては再利用
が困難であり、たとえ再利用を図るとしてもその処理に
コストがかかりすぎ現実的でなく、また堆肥化してこれ
を利用する場合にも分解にかなりの長時間を要するばか
りでなく、その間の悪臭が甚だしく、更には微生物が窒
素を消費するために窒素飢餓の状態になり易い。Therefore, when processing this type of waste, it is difficult to reuse it, and even if reuse is attempted, the processing cost is too high and it is impractical.Also, when it is composted and used, it does not decompose. Not only does this take a considerable amount of time, the foul odor during the process is extremely bad, and furthermore, microorganisms are likely to become nitrogen starved as they consume nitrogen.
本発明は、こうした腐敗性廃棄物を短時間かつ低コスト
で効率良く処理し、しかも腐敗性廃棄物中から肥効成分
としてカルシウム化合物を回収することのできる、腐敗
性廃棄物からのカルシウム化合物の回収方法を提供する
ことを目的とするものである。The present invention aims to efficiently process such perishable waste in a short time and at low cost, and to recover calcium compounds from the perishable waste as a fertilizing ingredient. The purpose is to provide a collection method.
(問題点を解決するための手段)
本発明は、上記した目的を達成するために、固液混合の
腐敗性廃棄物100重量部に対し、酸化カルシウムの含
有量が95%以上でかつ多孔性を有する高活性な生石灰
を主成分とする添加剤を5〜50重量部添加し、これら
を混合攪拌して反応させ、得られたスラリー状の物質を
乾燥させた後、燃焼させることによりカルシウム化合物
を回収する一方、上記燃焼に伴う熱を回収して再利用す
る点に特徴を有する。(Means for Solving the Problems) In order to achieve the above-mentioned objects, the present invention provides that the content of calcium oxide is 95% or more and the porous Add 5 to 50 parts by weight of an additive whose main component is highly active quicklime, mix and stir to react, dry the resulting slurry, and burn it to form a calcium compound. It is characterized by recovering and reusing the heat accompanying the combustion.
本発明が適用される腐敗性廃棄物としては、豚し尿(4
Aを含む)、鶏糞その他の家畜糞尿、動物血液、上下水
余剰汚泥、焼酎カスあるいはオカラカス等の食品製造工
場から排出される腐敗性残漬などがある。これらは、例
えば豚し尿の場合には通常86.5%〜94.5%、乾
燥鶏糞の場合には通常15〜30%、上下水余剰汚泥の
場合には通常75〜97%、食品工場の腐敗性残漬の場
合には通常75〜95%の水分をそれぞれ含んでおり、
本発明に用いるにあたっては水分が75〜97%の状態
に調整されることが望ましい。As the putrescible waste to which the present invention is applied, pig human waste (4
(including A), chicken manure and other livestock manure, animal blood, excess water and sewage sludge, and putrefactive residue discharged from food manufacturing factories such as shochu scum and okara scum. For example, in the case of pig human waste, it is usually 86.5% to 94.5%, in the case of dried chicken manure, it is usually 15 to 30%, in the case of excess water and sewage sludge, it is usually 75 to 97%, and in the case of food factories. In the case of perishable residue, it usually contains 75 to 95% moisture,
When used in the present invention, it is desirable that the moisture content be adjusted to 75 to 97%.
本発明では、添付したブロック図に見られるようにこう
した原材料に添加剤を添加し、混合攪拌して先ずスラリ
ー状の物質を得る。具体的には、上記した腐敗性の産業
廃棄物100重量部に対して所定の添加剤を5〜50i
fL量部加え、両者を反応させる。In the present invention, as shown in the attached block diagram, additives are added to these raw materials and mixed and stirred to first obtain a slurry-like substance. Specifically, 5 to 50 parts of the specified additive was added to 100 parts by weight of the above-mentioned putrescible industrial waste.
Add 1 part of fL and allow both to react.
添加剤は次の条件を具備する高活性な生石灰を主成分と
する。The additive is mainly composed of highly active quicklime that meets the following conditions.
■酸化カルシウムの含有率が高く(望ましくは95%以
上)、水酸化カルシウム、炭酸カルシウム及びその他の
物質の含有率が低いこと。■High content of calcium oxide (preferably 95% or more) and low content of calcium hydroxide, calcium carbonate and other substances.
尚、組成成分として酸化マグネシウムが少量(例えば5
%以下)含まれていても良い。In addition, a small amount of magnesium oxide (for example, 5
% or less) may be included.
■多孔性を有し、表面積及び比表面積が広大で、細孔組
織が高度に発達していること。■Porous, with a large surface area and specific surface area, and a highly developed pore structure.
■水に少量、例えば水約lθ〜15m1に1〜2gを接
触させたときに、優れた水分散性、即ち、全方向に相当
広く分散する性質を有すること。(2) When brought into contact with a small amount of water, for example, 1 to 2 g in about lθ to 15 ml of water, it has excellent water dispersibility, that is, it has the property of being dispersed fairly widely in all directions.
■水に中量、例えば水約15〜20m1に5〜10gを
添加したときに、数秒後に激しく反応して水蒸気を発生
させること。(2) When a medium amount is added to water, for example, 5 to 10 g to about 15 to 20 ml of water, a violent reaction occurs after a few seconds to generate water vapor.
■水に一定量、例えば水100m1に20gを添加した
ときに充分に反応し、理論値に近似した温度上昇が認め
られること。(2) When a certain amount of water is added, for example, 20 g to 100 ml of water, a sufficient reaction occurs and a temperature rise close to the theoretical value is observed.
■水と接触後の消石灰を主成分とするスラリーにおいて
、沈降速度が小、例えば上記■に記載した割合て添加し
、15分放置した状態において沈降現象が認められない
こと。(2) In a slurry whose main component is slaked lime after contact with water, the sedimentation rate is low, for example, no sedimentation phenomenon is observed when the slurry is added at the rate described in (2) above and left for 15 minutes.
上おした■乃至■の条件のうち、■乃至■は■及び■か
ら必然的に導かれ得る性質で、また■は■乃至■の条件
を満たしているかどうかを最終的にチエツクする際の条
件である。Among the above conditions ■ to ■, ■ to ■ are properties that can be inevitably derived from ■ and ■, and ■ is a condition for ultimately checking whether the conditions ■ to ■ are satisfied. It is.
この高活性な生石灰を主成分とする添加剤による反応時
間紘、長ずざると、練り現象(ペースト化、微細化)を
呈し、生成される土壌改良剤が団粒構造になりにくく、
また乾燥しにくくなることから、−数的には15分以内
が望ましい。但し、原材料中に、例えばリン脂質、液状
油分、塩基性物質、難分解性の高分子化合物などの反応
しにくい物質が含まれている場合には反応時間は適宜延
長される。尚、添加剤には5%以下のマグネシアが含ま
れていると、後述する燃焼残漬を肥料として利用すると
きにより有効である。また、添加剤を添加するにあたっ
ては、−度に上記した重量%のものを加えるのではなく
、多回に分けて、初めに反応し易いものとの反応を行わ
せ、次いで徐々に反応し難いものとの反応を行わせるよ
うにしても良い。If the reaction time of this highly active quicklime-based additive is too long, it will exhibit a kneading phenomenon (paste formation, fineness), and the resulting soil conditioner will be difficult to form agglomerated structures.
In addition, since it becomes difficult to dry, it is desirable that the drying time be within 15 minutes. However, if the raw materials contain substances that are difficult to react with, such as phospholipids, liquid oils, basic substances, and difficult-to-decompose polymer compounds, the reaction time may be extended as appropriate. It should be noted that if the additive contains 5% or less of magnesia, it will be more effective when the combustion residue, which will be described later, is used as fertilizer. In addition, when adding additives, instead of adding the additives in the above-mentioned weight percentage at once, divide the additives into multiple batches, first react with those that are easy to react, and then gradually react with those that are difficult to react with. It may also be made to react with things.
反応生成物として得られたスラリー状の物質は、有機性
廃棄物中に含まれていた水溶性リン酸の約97%が有効
態のリン酸カルシウムとして固定され、かつ、有機態リ
ン酸、リン脂質、グリセライドなどの難分解性成分を分
解して生成されるリン酸カルシウム及び脂肪酸カルシウ
ム並びにカルシウムが分散された有機体が含有されてい
る。In the slurry-like substance obtained as a reaction product, about 97% of the water-soluble phosphoric acid contained in the organic waste is fixed as active calcium phosphate, and organic phosphoric acid, phospholipids, It contains calcium phosphate and fatty acid calcium produced by decomposing persistent components such as glyceride, and an organic substance in which calcium is dispersed.
有効態のリン酸カルシウムは、腐敗性廃棄物中に存在す
る、主として水溶性リン酸及びリン脂質中に含まれるリ
ン酸と上記添加剤との反応によって生成される。従って
、原材料たる腐敗性廃棄物中に含まれていた水溶性リン
酸及び脂質が著しく減少している。Calcium phosphate in its active form is produced by the reaction of the above-mentioned additive with water-soluble phosphoric acid present in putrescible waste and phosphoric acid contained mainly in phospholipids. Therefore, the water-soluble phosphoric acid and lipids contained in the perishable waste, which is the raw material, are significantly reduced.
そして、生成されたスラリー状の物質は、湿潤状態また
け乾燥された後に燃焼される。燃焼にあたっては、少量
の助燃剤あるいけ可燃性の廃棄物を利用するようにして
も良い、可燃性の廃棄物としてオガ屑を含有した鶏糞を
用いると、鶏糞の燃焼残漬としてリン酸カルシウムなど
のカルシウム化合物をここでも有効に得ることができる
。The slurry-like material thus produced is wetted, dried, and then combusted. For combustion, a small amount of combustion improver or combustible waste may be used.If poultry manure containing sawdust is used as the combustible waste, calcium such as calcium phosphate may be used as the residue after burning the poultry manure. Compounds can also be obtained effectively here.
燃焼状態において、上記物質けその成分である上記した
有機化合物が煙を出しつつ伝播燃焼し、その燃焼残漬中
には炭酸カルシウム、リン酸カルシウム、酸化カルシウ
ム、少量の水酸化カルシウム、微量の金属酸化物等が含
まれる。これらの残漬は肥料として有効である。In the combustion state, the above-mentioned organic compounds, which are the components of the substance, propagate and burn while emitting smoke, and the combustion residue contains calcium carbonate, calcium phosphate, calcium oxide, a small amount of calcium hydroxide, and a small amount of metal oxide. etc. are included. These residues are effective as fertilizer.
また、生成物が燃焼される際に発生する熱は、原料スラ
リーや、反応生成物の予備乾燥用の熱源として利用した
り、熱交換器を介して温風あるいは温水として回収して
も良い。反応生成物の予備乾燥用の熱源として利用する
場合には、天候、風、温度あるいは季節に左右されるこ
となく乾燥が可能となる。燃焼時の排ガス中には通常5
〜12%の炭酸ガスが含まれており、この排ガスを反応
生成物中の水酸化カルシウムと反応させることにより、
炭酸カルシウムの生成を促して、反応処理物の乾燥速度
を向上させることができる。また、同様にして排ガスを
植物の成長促進に活用することも可能である。Further, the heat generated when the product is combusted may be used as a heat source for pre-drying the raw material slurry or the reaction product, or may be recovered as hot air or hot water via a heat exchanger. When used as a heat source for pre-drying reaction products, drying can be performed without being affected by weather, wind, temperature or season. Usually 5 is contained in the exhaust gas during combustion.
Contains ~12% carbon dioxide gas, and by reacting this exhaust gas with calcium hydroxide in the reaction product,
By promoting the production of calcium carbonate, the drying rate of the reaction product can be improved. It is also possible to utilize exhaust gas to promote plant growth in a similar manner.
(実施例) 以下、本発明の実施例を示す。(Example) Examples of the present invention will be shown below.
[実施例1]
本実施例と次の実施例では、先ず、腐敗性廃棄物に所定
の添加剤を添加してスラリー状の物質を反応生成するま
でを示す。[Example 1] In this example and the next example, first, a process will be shown in which a predetermined additive is added to putrescible waste and a slurry-like substance is reacted and produced.
原料として鶏糞、オガ屑及び豚し尿の混合成分から成る
水分85.0重量%のスラリー850Kgに対して、高
活性を有する生石灰を主成分とする添加剤を140Kg
([料に対して16.5重量%)添加し、特殊反応器内
で攪拌しつつ15分間反応させた。140 kg of an additive whose main component is quicklime with high activity is added to 850 kg of a slurry with a moisture content of 85.0% by weight, which is made of a mixture of chicken manure, sawdust, and pig excrement as raw materials.
(16.5% by weight based on the material) and reacted for 15 minutes with stirring in a special reactor.
上記の反応過程において、生石灰と水分との水和反応お
よび化学反応によって発生する反応熱によって、反応物
スラリーの温度は上昇し、温度上昇度(反応物スラリー
温度と原料スラリー温度の差)は46゜0℃であった。In the above reaction process, the temperature of the reactant slurry rises due to the reaction heat generated by the hydration reaction and chemical reaction between quicklime and water, and the degree of temperature rise (difference between the reactant slurry temperature and the raw material slurry temperature) is 46 It was 0°C.
得られた反応物スラリーを屋根付きハウス(強制通風施
設付)内で、大気と接触させつつ風乾させ、含水率38
.0重量%の反応生成物505にgを得た。The obtained reactant slurry was air-dried in a roofed house (equipped with forced ventilation facilities) while being in contact with the atmosphere until the moisture content was 38.
.. 505 g of 0% by weight reaction product was obtained.
原料中の水溶性リン酸含有量は11,200mg/にg
(乾量基準)であったのに対して、反応生成物中の当
該成分は59mg/にg(乾量基準)であった、また、
原料中の脂質含有量は39.200mg/Kg (乾
量基準)であったのに対して、反応生成物中の当該成分
は5.220rng/Kg (乾量基準)であった。The water-soluble phosphoric acid content in the raw material is 11,200mg/g
(on a dry basis), whereas the component in the reaction product was 59 mg/g (on a dry basis).
The lipid content in the raw material was 39.200 mg/Kg (dry basis), whereas the content of the component in the reaction product was 5.220 rng/Kg (dry basis).
従って、上記腐敗性廃棄物に対する本実施例による水溶
性リン酸の除去率(削減率)は99.5%、脂質の除去
率(削減率)は86.7%に相当し、こうした物質は、
反応物ステ1ナー中にカルシウム化合物他として含有さ
れる。Therefore, the removal rate (reduction rate) of water-soluble phosphoric acid in this example from the above-mentioned putrescible waste corresponds to 99.5%, and the removal rate (reduction rate) of lipids corresponds to 86.7%.
The reactant is contained in the stainer as a calcium compound, among other things.
[実施例2]
原料として豚し尿と余剰汚泥との混合成分から成る水分
86.9重量%のスラリー820にgに対して、高活性
を有する生石灰を主成分とする添加剤を96Kg(J!
;l料に対して11.7重量%)添加し、特殊反応器内
で攪拌しつつ8分間反応させた。[Example 2] 96 kg (J!
;11.7% by weight based on the total amount) and reacted for 8 minutes with stirring in a special reactor.
上記の反応過程において、生石灰と水分との水和反応お
よび化学反応によって発生する反応熱によって、反応物
スラリーの温度は上昇し、温度上昇度(反応物スラリー
温度と原料スラリー温度の差)は33℃であった。In the above reaction process, the temperature of the reactant slurry rises due to the reaction heat generated by the hydration reaction and chemical reaction between quicklime and water, and the degree of temperature rise (difference between the reactant slurry temperature and the raw material slurry temperature) is 33 It was ℃.
得られた反応物スラリーを屋根付きハウス内で大気と接
触させつつ風乾させ、含水率38.5重量%の反応生成
物308Kgを得た。The obtained reaction product slurry was air-dried in a roofed house while being in contact with the atmosphere to obtain 308 kg of a reaction product having a water content of 38.5% by weight.
原料中の水溶性リン酸含有量は12,200mg/Kg
(乾量基準)であったのに対して、反応生成物中の
当該成分は27mg/にg (乾量基準)であった。ま
た、原料中のアンモニア性窒素含有量は34、2oor
ng/Kg (乾量基準)であったのに対して、反応
生成物中の当該成分は281 mg/にg (乾ffl
′基準)であった。Water-soluble phosphoric acid content in raw materials is 12,200mg/Kg
(on a dry basis), whereas the amount of the component in the reaction product was 27 mg/g (on a dry basis). In addition, the ammonia nitrogen content in the raw material is 34.2oor
ng/Kg (dry basis), whereas the component in the reaction product was 281 mg/kg (dry basis).
'standard).
従って、上記した腐敗性廃棄物に対する本実施例による
水溶性リン酸の除去率(削減率)は99.8%、アンモ
ニア性窒素の除去率(削減率)は99.2%に相当し、
こうした物質は、反応物スラリー中にカルシウム化合物
他として含有される。Therefore, the removal rate (reduction rate) of water-soluble phosphoric acid in this example for the above-mentioned putrescible waste corresponds to 99.8%, and the removal rate (reduction rate) of ammonia nitrogen corresponds to 99.2%.
Such materials are included in the reactant slurry as calcium compounds and others.
[実施例3]
次に、上記実施例のようにして得られた反応物スラリー
を燃焼する実施例を示す。[Example 3] Next, an example will be shown in which the reactant slurry obtained as in the above example is burned.
燃焼にあたっては、乾燥鶏糞(水分15%〜30%、オ
ガ屑40〜60%)を燃料とし、少量の廃油を助燃剤と
して予め含浸(約2〜3%)させるか、あるいは、死人
もしくは少量の可燃性燃料を用いることにより、乾燥鶏
糞中の可燃性成分を燃焼させる。その際に発生する燃焼
熱は、湿潤状態の反応生成物(ケーキ状)を乾燥させる
熱源として利用することができる。For combustion, dry chicken manure (moisture 15% to 30%, sawdust 40 to 60%) is used as fuel, and a small amount of waste oil is impregnated in advance as a combustion improver (approximately 2 to 3%), or a dead person or a small amount of By using flammable fuel, combustible components in dried chicken manure are burned. The combustion heat generated at this time can be used as a heat source for drying the wet reaction product (cake-like).
反応生成物を乾燥させる場合、炭酸ガスを多量(5〜1
5%)含む燃焼排気を直接に反応生成物ケーキと接触さ
せる方法と適当な熱交換器などを用いて、加湿空気を用
いて乾燥させる方法があるが、熱的にも、また、炭酸ガ
スによって反応生成物ケーキに残留する消石灰が反応し
て炭酸カルシウムを形成することからも、直接接触法が
有利である。When drying the reaction product, a large amount of carbon dioxide gas (5 to 1
There are two methods: one is to bring the combustion exhaust containing 5%) into direct contact with the reaction product cake, and the other is to dry it using humidified air using an appropriate heat exchanger. The direct contact method is also advantageous because the slaked lime remaining in the reaction product cake reacts to form calcium carbonate.
反応生成物ケーキは、乾燥が進むと昇温され、遂に着火
し、緩やかに燃焼し始める。この燃焼状態は空気量によ
って相当程度調節できる。As the reaction product cake continues to dry, its temperature increases, and it finally ignites and begins to burn slowly. This combustion state can be adjusted to a considerable extent by changing the amount of air.
また、この燃焼によって発生する熱を新たな反応生成物
ケーキと接触させ、有効に利用することはもちろん可能
である。Furthermore, it is of course possible to make effective use of the heat generated by this combustion by bringing it into contact with a new reaction product cake.
水分45.0〜53.0%を含有する反応生成物ケーキ
に対し、可燃性廃油を水分25.0%の乾燥鶏糞に対し
、重量で3%はぼ均一に添加し、金属性ネット上で乾燥
し、引続いて乾燥反応生成物を燃焼させた。燃焼前の反
応生成物中の脂質は10、400〜11.400mg/
kg (乾量基準)であったが、燃焼後の残漬では28
0〜1.480rrrg/kg (乾量基準)に低下し
た。To the reaction product cake containing 45.0 to 53.0% moisture, 3% by weight of combustible waste oil was evenly added to dried chicken manure with a moisture content of 25.0%, and the mixture was heated on a metal net. After drying, the dry reaction product was subsequently combusted. The lipid content in the reaction product before combustion is 10,400 to 11,400 mg/
kg (dry basis), but the residue after combustion was 28
It decreased to 0 to 1.480 rrrg/kg (dry weight basis).
一方、反応生成物中の全リン酸が2,43〜2.75%
(乾量基準)であったものが、残漬中では、可燃性成分
が燃焼されるので、全リン酸として、4.18〜6.2
8%(軽量基準)に濃縮されたリン酸はリン酸カルシウ
ムとして残留し、その他の主成分として炭酸カルシウム
などが共存していることが考えられる。On the other hand, the total phosphoric acid in the reaction product is 2.43-2.75%
(dry basis), but in the residual soaking, combustible components are burned, so total phosphoric acid is 4.18 to 6.2
It is thought that phosphoric acid concentrated to 8% (light weight standard) remains as calcium phosphate, and other main components such as calcium carbonate coexist.
このような方法により、炭酸カルシウムやカルシウム化
合物中に、比較的高含有率でリン酸カルシウムが含まれ
た反応生成物を得ることが可能である。By such a method, it is possible to obtain a reaction product containing a relatively high content of calcium phosphate in calcium carbonate or a calcium compound.
なお、原料中に全リン酸が多量含まれる場合には上記の
方法により得られる反応生成物中のリン酸カルシウムの
量は当然高含有率となる。Note that when the raw materials contain a large amount of total phosphoric acid, the amount of calcium phosphate in the reaction product obtained by the above method will naturally be high.
次に、上記した実施例に基づいて得られた燃焼残漬とし
てのカルシウム化合物(以下、単に残漬という)を用い
た場合の施肥例を示す。Next, an example of fertilization using a calcium compound as a combustion residue (hereinafter simply referred to as residue) obtained based on the above-described example will be shown.
[実施例4]
本実施例は、ハウス内でポット試験を行なった一例を示
す。[Example 4] This example shows an example in which a pot test was conducted in a greenhouse.
1 Q 0m2(17−Jl/)当り、上記残渣を20
0にg添加し、深さ約12cmにわたってほぼ均一にな
るように土壌と混合した。なお、市販の化学肥料を基礎
肥料として添加した。20 of the above residue per 1 Q 0m2 (17-Jl/)
0g was added to the soil and mixed with the soil so that it was almost uniform over a depth of about 12 cm. Note that a commercially available chemical fertilizer was added as a basic fertilizer.
方、対照区については、残渣を添加しないで、同一割合
で市販の化学肥料を添加し、対比試験を行った。On the other hand, for the control plot, a commercially available chemical fertilizer was added in the same proportion without adding any residue, and a comparative test was conducted.
作物ホウレン草の場合の残漬添加区と対照区を対比して
次に示す。A comparison of the residue-added plot and the control plot for the spinach crop is shown below.
1作目
(株密度 5株/1ボット、プラスチック製5号鉢)
残漬添加区 対照区
重量 87.3g 71.9g本実施例に
よれば、初年度において、重量の多い作物を得ることが
できた。1st crop (plant density 5 plants/1 bot, plastic No. 5 pot) Residue addition control control weight 87.3g 71.9g According to this example, it was possible to obtain a heavy crop in the first year. did it.
[実施例5]
面記実施例より得られた残渣を、露地Zoom2(1ア
ール)当り150に6加し、深さ約100cmにわたっ
てほぼ均一になるように土壌と混合した。尚、市販の化
学肥料を基礎肥料として添加した。[Example 5] The residue obtained in the above example was added to 6 to 150 per Zoom 2 (1 are) of open ground, and mixed with soil so that it was almost uniform over a depth of about 100 cm. A commercially available chemical fertilizer was added as a basic fertilizer.
一方、対照区については、上記改良材を添加しないで、
同一割合で市販の化学肥料を添加し、対比試験を行った
。On the other hand, for the control plot, the above improvement materials were not added.
A comparative test was conducted by adding commercially available chemical fertilizers in the same proportions.
作物として長いもを採用し、これを添加区と対照区を対
比して次に示す。Long yam was used as the crop, and the following shows a comparison between the additive plot and the control plot.
初年度
反応物添加区 対照区
重量/木 834g 502g品質(3L)
11% O%
本実施例によれば、本残漬を添加した場合の方が重量、
品質共に優れた長いもを得ることができた。First year reactant addition control control weight/wood 834g 502g quality (3L)
11% O% According to this example, the weight and
I was able to obtain long pieces of excellent quality.
[実施例6コ
前記実施例の残漬を、露地100m2(1アール)当り
75に6加し、深さ約12cmにわたってほぼ均一にな
るように土壌と混合した。尚、市販の化学肥料を基礎肥
料として添加した。[Example 6] The residue from the above example was added to 75 to 6 per 100 m2 (1 are) of open ground, and mixed with soil so that it was almost uniform over a depth of about 12 cm. A commercially available chemical fertilizer was added as a basic fertilizer.
一方、対照区については、改良材を添加しないで、同一
割合で市販の化学肥料を添加し、対比試験を行った。On the other hand, for the control plot, a commercially available chemical fertilizer was added in the same proportion without adding any improvement material, and a comparative test was conducted.
作物としてにんにくを採用し、これを添加区と対照区に
分けて耕作した結果を対比して次に示す。Garlic was used as a crop, and the results of cultivating it divided into additive plots and control plots are shown below.
初年度
添加区 対照区
球重量/株 151.5g 130.0g品質
(2L球/10球) 10 8本実施例から
明らかなように、添加区の方が重量、品質共に優れたに
んにくを得ることができた。First year addition group Control group Bulb weight/plant 151.5g 130.0g Quality (2L bulbs/10 bulbs) 10 8 As is clear from this example, the addition group produces garlic that is superior in both weight and quality. was completed.
[実施例7]
前記実施例に係る残漬を、土壌、ハウスJOOm2(1
アール)当り、300に6加し、深さ約120cmにわ
たフてほぼ均一になるように土壌と混合し、市販の化学
肥料を基礎肥料として添加した。[Example 7] The residue according to the above example was applied to soil, house JOOm2 (1
6 per area) was added to 300 and mixed with soil to a depth of about 120 cm so that it was almost uniform, and a commercially available chemical fertilizer was added as a basic fertilizer.
一方、対照区については、改良材を添加しないで、同一
割合で市販の化学肥料を添加し、対比試験を行った。On the other hand, for the control plot, a commercially available chemical fertilizer was added in the same proportion without adding any improvement material, and a comparative test was conducted.
作物ゴボウの場合の添加区と対照区を対比して次に示す
。A comparison of the added area and the control area for the burdock crop is shown below.
(初年度)
添加区 対照区
長さ 100〜120cm 70〜90cm太さ
2〜2. 5ca+ 1〜1 、 5cm色
調 淡褐色を帯びた白色 茶褐色
鮮度保持 30日以上 15日以内(2年度)
添加区 対照区
長さ 100〜130c+s 60〜90cm太さ
2〜2. 5CIII O18〜1.5C11根
枝根(細根)多くて長い 枝根(細根)少くて短い
色調 淡褐色を帯びた白色 茶褐色
鮮度保持 30日以上 15日以内本実施例によ
れば、初年度はいうに及ばず、2年度においても木残漬
を加えた方が収穫に良好な結果を得ていることが解る。(First year) Addition area Control area Length 100-120cm Thickness 70-90cm
2-2. 5ca+ 1~1, 5cm Color tone White with light brown Brown freshness retention 30 days or more Within 15 days (2 years) Added area Control area Length 100~130c+s 60~90cm Thickness
2-2. 5CIII O18-1.5C11 Roots Many and long branches and roots Few and short branches and roots (fine roots) Color tone Light brownish white Brownish freshness retained More than 30 days Within 15 days According to this example, in the first year However, it can be seen that the addition of wood residue produced better results in the second year as well.
[実施例8]
前記実施例2より得られた残漬を、土壌100m2(1
アール)当り、200欣添加し、深さ約25CII+に
わたってほぼ均一になるように土壌と混合し、市販の化
学肥料を基礎肥料として添加した。[Example 8] The residue obtained in Example 2 was added to 100 m2 (1
200 cents per R) was added and mixed with the soil so as to be almost uniform over a depth of about 25 CII+, and a commercially available chemical fertilizer was added as a basic fertilizer.
一方、対照区については、上記改良材を添加しないで、
同一割合 で市販の化学肥料を添加し、対比試験を行っ
た。On the other hand, for the control plot, the above improvement materials were not added.
A comparative test was conducted by adding commercially available chemical fertilizers in the same proportions.
作物ナスの場合の結果を、反応物添加区と対照区を対比
して次に示す。The results for the eggplant crop are shown below, comparing the reactant-added plot and the control plot.
(初年度)
反応物添加区 対照区
個数(収穫期当り)320個 120個収穫期間
150日 120日(2年度)
反応物添加区 対照区
個数(収穫期当り)350個 130個収穫期間
155日 125日本実施例によれば、実施例7と
同様に2年度目においてもこの残漬が作物の成長に有効
に作用していることが解る。(First year) Reactant addition area Control area Number of items (per harvest period) 320 items 120 items Harvest period
150 days 120 days (2 years) Reactant addition area Control area Number of pieces (per harvest period) 350 pieces 130 pieces Harvest period
155 days 125 According to the Japanese example, it can be seen that this residual pickling has an effective effect on the growth of crops in the second year as well as in Example 7.
(発明の効果)
以上述べたように、本発明によれば、固液混合の腐敗性
廃棄物に高活性な生石灰を主成分とする所定の添加剤を
加えて反応させ、得られたスラリー状物質を燃焼させる
ようにしているので、腐敗性廃棄物中に含まれる全リン
酸の大部分が有効態のリン酸カルシウムとして安定され
、水溶性リン酸が元の量の3%以下に減少することとな
り、未反応残留物による害虫発生や有害微生物等を発生
させたり、悪臭を発生させたりすることなく、腐敗性廃
棄物を低コストで効率良く処理できる。(Effects of the Invention) As described above, according to the present invention, a predetermined additive containing highly active quicklime as a main component is added to solid-liquid mixed putrescible waste, and the resulting slurry is reacted. By burning the material, most of the total phosphoric acid contained in the putrescible waste is stabilized as active calcium phosphate, and water-soluble phosphoric acid is reduced to less than 3% of its original amount. , perishable waste can be efficiently processed at low cost without causing pests, harmful microorganisms, etc. due to unreacted residues, or producing bad odors.
また、本発明によれば、上記反応スラリーを燃焼させる
ので、腐敗性廃棄物中から肥効成分として有効なカルシ
ウム化合物のみを回収することができるゆこのカルシウ
ム化合物は、肥料として見たときに、遅効性、緩効性、
疎水性及び吸水性に優れ、持続性を有する。Furthermore, according to the present invention, since the reaction slurry is combusted, only the calcium compound that is effective as a fertilizer component can be recovered from the putrescible waste.When viewed as a fertilizer, Yuko's calcium compound is slow-acting, slow-acting,
It has excellent hydrophobicity and water absorption, and is long lasting.
更に、本発明によれば、反応スラリーを燃焼する際の熱
を、反応スラリーの乾燥などの熱源として再利用でき、
熱の有効利用が可能となる利点を有するものである。Furthermore, according to the present invention, the heat generated when burning the reaction slurry can be reused as a heat source for drying the reaction slurry, etc.
This has the advantage that heat can be used effectively.
図は、本発明方法の工程を示すブロック図である。 The figure is a block diagram showing the steps of the method of the invention.
Claims (8)
酸化カルシウムの含有量が95%以上でかつ多孔性を有
する高活性な生石灰を主成分とする添加剤を5〜50重
量部添加し、これらを混合攪拌して反応させ、得られた
スラリー状の物質を乾燥させた後、燃焼させることによ
りカルシウム化合物を回収する一方、上記燃焼に伴う熱
を回収して再利用することを特徴とする腐敗性廃棄物か
らのカルシウム化合物の回収方 法。(1) For 100 parts by weight of solid-liquid mixed putrescible waste,
Add 5 to 50 parts by weight of a highly active quicklime-based additive with a calcium oxide content of 95% or more and porosity, mix and stir to react, and create a slurry. A method for recovering calcium compounds from putrescible waste, comprising recovering calcium compounds by drying a substance and then burning it, while recovering and reusing the heat accompanying the combustion.
炭酸カルシウムとを含むものであることを特徴とする、
特許請求の範囲第1項記載の腐敗性廃棄物からのカルシ
ウム化合物の回収方法。(2), wherein the calcium compound contains calcium phosphate and calcium carbonate;
A method for recovering calcium compounds from putrescible waste according to claim 1.
尿を含浸させて堆肥化させたもの、あるいは醗酵途上中
にあるものであることを特徴とする特許請求の範囲第1
項記載の腐敗性廃棄物からのカルシウム化合物の回収方
法。(3) The perishable waste is sawdust, bark impregnated with livestock human waste and composted, or in the process of fermentation.
Method for recovering calcium compounds from putrescible waste as described in Section 1.
間的反応特性と、水との反応時に理論値に近い昇温特性
とを有することを特徴とする特許請求の範囲第1項記載
の腐敗性廃棄物からのカルシウム化合物の回収方法。(4) The additive has excellent water dispersion properties, instantaneous reaction properties with water, and temperature increase properties close to theoretical values upon reaction with water. The method for recovering calcium compounds from putrescible waste according to item 1.
ていることを特徴とする特許請求の範囲第1項記載の腐
敗性廃棄物からのカルシウム化合物の回収方法。(5) The method for recovering calcium compounds from putrescible waste as set forth in claim 1, wherein the additive contains 5% or less of magnesia.
、燃焼排気中の顕熱、水蒸気潜熱を前記添加剤混合前の
腐敗性廃棄物の予熱に利用し、また、燃焼排気中の炭酸
ガスを植物の成長促進に利用することを特徴とする、腐
敗性廃棄物からのカルシウム化合物の回収方法。(6) In the combustion process according to claim 1, sensible heat and steam latent heat in the combustion exhaust are used to preheat the perishable waste before mixing the additive, and carbon dioxide in the combustion exhaust is used. A method for recovering calcium compounds from putrescible waste, characterized in that gas is used to promote plant growth.
、燃焼排気を燃焼前の反応物の乾燥に利用することを特
徴とする、腐敗性廃棄物からのカルシウム化合物の回収
方法。(7) A method for recovering calcium compounds from putrescible waste, characterized in that in the combustion process according to claim 1, combustion exhaust gas is used to dry reactants before combustion.
、燃焼排気を熱交換器を介して温水または温風を得るよ
うにしたことを特徴とする、腐敗性廃棄物からのカルシ
ウム化合物の回収方法。(8) In the combustion process described in claim 1, hot water or hot air is obtained from the combustion exhaust through a heat exchanger. Collection method.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1087744A JPH02265700A (en) | 1989-04-06 | 1989-04-06 | Recovery of calcium compound from putrefactive waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1087744A JPH02265700A (en) | 1989-04-06 | 1989-04-06 | Recovery of calcium compound from putrefactive waste |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH02265700A true JPH02265700A (en) | 1990-10-30 |
Family
ID=13923444
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1087744A Pending JPH02265700A (en) | 1989-04-06 | 1989-04-06 | Recovery of calcium compound from putrefactive waste |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH02265700A (en) |
-
1989
- 1989-04-06 JP JP1087744A patent/JPH02265700A/en active Pending
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