JPS61203195A - Preparation of soil conditioner - Google Patents

Preparation of soil conditioner

Info

Publication number
JPS61203195A
JPS61203195A JP60041802A JP4180285A JPS61203195A JP S61203195 A JPS61203195 A JP S61203195A JP 60041802 A JP60041802 A JP 60041802A JP 4180285 A JP4180285 A JP 4180285A JP S61203195 A JPS61203195 A JP S61203195A
Authority
JP
Japan
Prior art keywords
soil
soil conditioner
test
sludge
granules
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.)
Granted
Application number
JP60041802A
Other languages
Japanese (ja)
Other versions
JPH045709B2 (en
Inventor
Kouzou Oonuki
大貫 黄三
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP60041802A priority Critical patent/JPS61203195A/en
Publication of JPS61203195A publication Critical patent/JPS61203195A/en
Publication of JPH045709B2 publication Critical patent/JPH045709B2/ja
Granted legal-status Critical Current

Links

Classifications

    • 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
    • Y02P20/10Process efficiency
    • Y02P20/133Renewable energy sources, e.g. sunlight

Landscapes

  • Soil Conditioners And Soil-Stabilizing Materials (AREA)
  • Fertilizers (AREA)

Abstract

PURPOSE:To prepare a soil conditioner with excellent soil conditioning and plant growth promoting effects at a low cost through utilization of sludge of construction work which is troublesome to dispose, by granulating preheated sludge of construction work and bringing the granules into contact with a high temp. gas for burning. CONSTITUTION:Sludge of construction work having a water content of 80% or higher (e.g. muddy waste water produced by spot pile driving) is predried to an average water content of 30-60% by drying in the sun and/or open air storage for dehydration and is formed into granules of about 1-10 mm in diameter by means of an appropriate granulating machine. The granules are brought into contact with a gas at 500-1,100 deg.C in a rotary kiln for burning, sterilization and drying to produce a soil conditioner having a water content of 20-40%, a lime content of 5-8%, a magnesium oxide content of 0.5-0.7%, a pH of 9 or higher and cation exchanging ability.

Description

【発明の詳細な説明】 産業上の利用分野 本発明は、建設汚泥(橋梁・高架橋工事、鉄筋・鉄骨・
コンクリート・石造建屋の新築工事などの建設工事にお
いて、場所打杭工法などで生ずる廃泥水をいう)から製
造される土壌改良剤の製造方法に関するものである。
[Detailed description of the invention] Industrial application field The present invention is applicable to construction sludge (bridge/viaduct construction, reinforcing bars/steel frames,
This invention relates to a method for producing a soil conditioner made from waste mud water generated from cast-in-place pile construction during construction work such as new construction of concrete and stone buildings.

従来の技術 近年、産業廃棄物の処理に困窮し、また省資源、省エネ
ルギーの観点から4その再利用の開発が急務とされてい
る。
BACKGROUND OF THE INVENTION In recent years, it has become difficult to dispose of industrial waste, and there is an urgent need to develop ways to reuse it from the viewpoint of resource and energy conservation.

上記建設汚泥も、もとより産業廃棄物の1aiであり、
特にその莫大な発生量及び廃泥水という状態のためにそ
の処理には困窮しており、莫大な費用を投じて処理して
いるのが現状であり、その再利用についての有効な提案
は伺らなされていない。
The construction sludge mentioned above is of course industrial waste 1ai,
In particular, it is difficult to treat it due to the huge amount generated and the state of waste mud water, and the current situation is that it costs a huge amount of money to dispose of it, and there are no effective proposals for its reuse. Not done.

一方、一般に土壌改良剤としては鉱物を主体としたもの
が知られているが、その用途上大量に使用されるため、
より安価な原料の開発が望まれている。
On the other hand, mineral-based soil improvers are generally known, but because they are used in large quantities for their purpose,
The development of cheaper raw materials is desired.

発明が解決しようとする問題点 従って、本発明の目的は、前記したその処理に困窮して
いる建設汚泥の有効利用を図り、上記鉱物を主体とする
土壌改良剤に代替しつる品質を有する土壌改良剤を建設
汚泥から極めて安価に製造することにある。
Problems to be Solved by the Invention Therefore, the purpose of the present invention is to effectively utilize the construction sludge described above, which is difficult to process, and to replace it with a soil conditioner mainly composed of the minerals mentioned above, and to produce soil with vine quality. The object of the present invention is to produce an improver from construction sludge at an extremely low cost.

問題点を解決するための手段 上記本発明の目的は、建設汚泥を予備乾燥した後、造粒
成型し、高温ガス接触により焼成する方法によって達成
される。このようにして得られる土壌改良剤は、植物に
対する害もなく、土壌改良及び植物栽培における効果も
従来の土壌改良剤に匹敵するものであり、充分にその代
替材として有用である。
Means for Solving the Problems The above objects of the present invention are achieved by a method in which construction sludge is pre-dried, granulated, and calcined by contact with high-temperature gas. The soil conditioner thus obtained is harmless to plants, and its effects on soil improvement and plant cultivation are comparable to those of conventional soil conditioners, making it fully useful as a substitute.

発明の態様 次に、本発明の土壌改良剤の製造方法について、その工
程毎に詳細に説明する。
Aspects of the Invention Next, each step of the method for producing the soil conditioner of the present invention will be explained in detail.

(cL)予備乾燥 まず、建設汚泥を予備乾燥して、造粒し易い含水量に乾
燥する。一般に建設汚泥Figo%以上の含水量を有し
、これを使用する造粒機のタイプに応じて平均水分的3
0〜60%程度、好ましくは約40チ程度まで乾燥する
(cL) Pre-drying First, construction sludge is pre-dried to a moisture content that makes it easy to granulate. Construction sludge generally has a water content of Figo% or higher, with an average moisture content of 3% depending on the type of granulator in which it is used.
Dry to about 0 to 60%, preferably about 40 inches.

この予備乾燥は、所望の方法が採用できるが、その莫大
な処理量を考膳すれば、実際上は図面に示すフローシー
トのように、天日乾燥及び/又は野積保管脱水による方
法が好適である。天日乾燥は、薄く積層することにより
、天日による脱水を行なうものであり、一方、野積保管
脱水は建設汚泥を貯溜槽に貯溜(表面はシート養生)す
ることにより、汚泥中に含まれる水分を重力沈降と1部
表面よりの蒸発により脱水するものであり、両方法を採
用する場合にはいずれを先に行なってもよい。通常、約
gssの含水量の建設汚泥は約13日の天日乾燥で平均
水分的50%に、その後の野積保管(約24日)により
40%以下に脱水される。
Any desired method can be used for this pre-drying, but considering the huge amount of processing involved, it is actually preferable to use solar drying and/or open storage dehydration as shown in the flow sheet shown in the drawing. be. In solar drying, dehydration is carried out under the sun by layering the sludge thinly.On the other hand, in open storage dehydration, construction sludge is stored in a storage tank (the surface is covered with a sheet), and the moisture contained in the sludge is removed. The water is dehydrated by gravity sedimentation and partial evaporation from the surface, and if both methods are employed, either method may be performed first. Normally, construction sludge with a water content of about GSS is dehydrated to an average moisture content of 50% by drying in the sun for about 13 days, and to less than 40% by subsequent storage in the open (about 24 days).

(句 造粒成型 以上のように予備乾燥された建設汚泥は、次いで適当な
造粒機により所望の粒量に造粒、成型すfる。造粒機と
しては、転勤形、押出し成型形など穐々のものが使用で
きる。中間工程として行なわれるタイプの造粒機の場合
には、さらに成型工程を付加してもよい。粒子径として
は、土壌改良剤としての目的からみて、約1〜1゜■、
好ましくは5〜6m程度が望ましい。
(Pelletization and molding) The construction sludge pre-dried as described above is then granulated and molded into the desired granule amount using an appropriate granulator. Examples of granulators include transfer type, extrusion type, etc. In the case of a type of granulator that performs this as an intermediate step, a molding step may be added.The particle size is approximately 1 to 1,000 yen, considering the purpose of the soil conditioner. 1゜■,
Preferably about 5 to 6 m is desirable.

CC)焼成 造粒された建設汚泥は、次いで高温、例えば約500〜
1100℃、好ましくは約800〜+00’cの高温ガ
スに接触せしめて、造粒物の焼成を行なうと同時に殺菌
消毒及び乾燥を行なう。この焼成工程は、実際上はロー
タリーキルンを用いて行なうのが好適である。。
CC) The calcined granulated construction sludge is then heated to a high temperature, e.g.
The granulated material is brought into contact with a high temperature gas of 1100 DEG C., preferably about 800 DEG to +00 DEG C., to sterilize and dry the granulated material at the same time as firing it. In practice, this firing step is preferably carried out using a rotary kiln. .

以上のようにして、使用建設汚泥に応じて水分的20〜
40%、石灰公約5〜8qb、苦土約0.5〜0.7 
To 、 pH9以上の陽イオン交換能力を有する土壌
改良剤が得られる。得られた土壌改良剤は、その後冷却
(自然冷却あるいは強制冷却のいずれでもよい)、検量
、計tSを経て製品として出荷される。
As described above, depending on the construction sludge used, the water content is 20~20~
40%, about 5-8 qb of lime, about 0.5-0.7 magnesium
To, a soil conditioner having a cation exchange ability of pH 9 or higher is obtained. The obtained soil conditioner is then cooled (natural cooling or forced cooling may be used), weighed, and subjected to total tS before being shipped as a product.

なお、焼成工程の熱源たる主燃料としては、廃タイヤを
使用することが省資源、省エネルギーの観点から有用で
ある。例えば、図面に示すように、ガス乾留発生炉に廃
タイヤを定量投入し、乾留ガス燃焼方式による高温燃焼
ガスを発生せしめ、ガス流量制御により温度制御を行な
う。燃料は完全に燃焼後白化した灰状になるまで処理を
施す。かかる処理により後処理は容易となり、排気は排
煙集塵機勢の設置により大気汚染対策を施す。
Note that it is useful to use waste tires as the main fuel that is the heat source in the firing process from the viewpoint of resource and energy conservation. For example, as shown in the drawing, a fixed amount of waste tires are charged into a gas carbonization generating furnace, high temperature combustion gas is generated by a carbonization gas combustion method, and temperature is controlled by controlling the gas flow rate. After the fuel is completely burned, it is treated until it becomes a white ash. Post-processing is facilitated by such treatment, and air pollution countermeasures are taken by installing exhaust gas and dust collectors.

実施例 以下、実施例及び試験例を示して本発明について具体的
に説明する。
EXAMPLES Hereinafter, the present invention will be specifically explained with reference to Examples and Test Examples.

実施例 平均水分86%の建設汚泥(四ツ街道中央興産)を天日
乾燥及び野積保管脱水して40%以下の含水量となるよ
うに予備乾燥した後、造粒機により平均して約5〜6■
の粒子となるように造粒した。これを、予めToRo式
ガス燃ガス燃焼加熱されたロータリーキルンを通過せし
め、800〜1000℃の高温ガス接触により焼成及び
殺   □困消毒し、その後冷却して本発明による土壌
改良剤を得た。
Example Construction sludge with an average moisture content of 86% (Yotsukaido Chuo Kosan) was dried in the sun, stored in an open area, dehydrated, pre-dried to a moisture content of 40% or less, and then granulated using a granulator to reduce the moisture content to about 5% on average. ~6■
It was granulated to obtain particles of . This was passed through a ToRo type rotary kiln which had been previously heated by burning gas, and was burned and sterilized by contact with high-temperature gas at 800 to 1000°C, and then cooled to obtain a soil conditioner according to the present invention.

該土壌改良剤の分析結果は以下のとおりであった◎ 水分(H,0)     27.98 %石灰全量(C
ab)    5.46%苦土全量(MIIO)   
 Q、56チ陽イオン交換容量 31 、3 maq/
乾±tooIIpH<現物5 ll1500 ad、 
16℃)   10.6試験例1(栽培試験) 上記実施例で得られた土壌改良剤の施用による、こ1つ
なの発芽並びに発芽後の生育への支障の有無及びその程
度を知るため、幼植物試験を実施した。その試験条件及
び結果を以下に示す。
The analysis results of the soil conditioner were as follows: ◎ Moisture (H,0) 27.98% Total amount of lime (C
ab) 5.46% total amount of magnesia (MIIO)
Q, 56 cation exchange capacity 31, 3 maq/
Dry ± too II pH < spot 5 ll1500 ad,
16°C) 10.6 Test Example 1 (Cultivation Test) In order to find out whether and to what extent the application of the soil conditioner obtained in the above example would cause problems with germination and post-germination growth, A plant test was conducted. The test conditions and results are shown below.

(リ 試験条件 (イ)供試試料及び対照試料の種類もしくは名称並びに
その分析成績は表−1のとおりである。
(i) Test conditions (a) The types or names of the test samples and control samples and their analytical results are as shown in Table-1.

表 −1 (ロ)供試圧壊の土性、沖積土又は洪積士の別等表 −
2 (ハ)供試作物の種類及び品種 こまつな に)施肥の設計及び試験区の名称 衣 −3 注1. 対照試料のCaO及びMliO(7)施用には
Table-1 (b) Soil properties of test crushing, alluvial soil or diluvial soil -
2 (c) Types and varieties of test crops (Komatsu Nani) Fertilization design and name of test area -3 Note 1. For control sample CaO and MliO(7) applications.

それぞれ試験区の供試試料の施用成分量に相当する量の
炭酸カルシウム及び炭酸マグネシウムを使用した。
Calcium carbonate and magnesium carbonate were used in amounts corresponding to the applied component amounts of the test samples in each test area.

注2 上記表に記載した供試、対照の両試料の施用量及
び成分量のほかに、標準区を含めたすべての試験区に、
N、P、O,及びに、0として、それぞれ25jlF、
50”F及び25111PK相当する量の硫酸アンモニ
ア、過りん酸石灰及び塩化別車を施用した(標準区Bは
三要素肥料の施用だけである)。
Note 2 In addition to the application amounts and component amounts for both the test and control samples listed in the table above, the following values were applied to all test plots including the standard plot:
25jlF as N, P, O, and 0, respectively.
Ammonia sulfate, lime superphosphate, and chloride were applied in amounts equivalent to 50"F and 25111PK (Standard Area B only applied ternary fertilizers).

(ホ)栽培方法 表  −4 (2)管理の状況 土壌光てん  施肥口 (3)試験のlFj来 発芽は、はfli2日後に開始し、供試及び対照の両試
料間に発芽開始日の差は見られなかった。
(e) Cultivation method table -4 (2) Management status Soil light fertilizer application port (3) Germination after 1Fj in the test started 2 days after fli, and there was a difference in the start date of germination between the test and control samples. was not seen.

供試及び対照の両試料区とも、発芽後の初期生育では目
立つ友生育差はなかったが、日数経過に従って供試試料
区の生育が対照試料より若干勝り、この生育差は収fy
4:lF時の生体重にも影響していた。調査酸#を表−
5に示す。
In both the test and control sample plots, there was no noticeable difference in growth in the early stages after germination, but as the number of days passed, the growth in the test sample plot slightly exceeded that of the control sample, and this growth difference was due to convergence.
The live weight at 4:1F was also affected. Table of investigation acid #
5.

以下余白 表−5:発芽及び生育調査成績 以上の試験結果から明らかなように、本発明の建設汚泥
から製造した土壌改良剤の施用によるこまつなの発芽及
びその後の生育は、炭酸カルシウム及び炭酸マグネシウ
ムを併用した対照肥料によるものと同等又は以上の成績
を示し、植生上支障のある成績は認められなかった。
Table 5: Germination and Growth Survey Results As is clear from the above test results, the germination and subsequent growth of Komatsuna by applying the soil conditioner produced from the construction sludge of the present invention is significantly affected by calcium carbonate and magnesium carbonate. Results were equal to or better than those obtained with the control fertilizer used in combination, and no adverse effects on vegetation were observed.

試験例2(土壌の酸度矯正試験) 本発明による土壌改良剤の酸度矯正力を知るため、2種
類の異なった土壌を用いて試験した。
Test Example 2 (Soil acidity correction test) In order to find out the acidity correction ability of the soil conditioner according to the present invention, a test was conducted using two different types of soil.

(1)試験方法 +00 gLtのビーカーに供試土壌と前記実施例で製
造された土壌改良剤を一定の割合にとり、よく混合した
後、水を加えて畑地状態(最大容水量の約60%)に調
節し、アルミニウムはくにて覆い、27℃の恒温器中に
入れ、所定の調査日ごとに取り出しこれに50−の水を
加えて、ガラス俸にて時々攪拌して1時間以上放置した
後、その上澄み液についてpHを測定した。
(1) Test method: Put the test soil and the soil conditioner produced in the above example in a certain ratio in a +00 gLt beaker, mix well, and then add water to the field condition (approximately 60% of the maximum water capacity). The mixture was then covered with aluminum foil, placed in a thermostat at 27°C, and taken out every designated survey day, and 50% water was added thereto.The mixture was stirred occasionally with a glass bowl and allowed to stand for over 1 hour. The pH of the supernatant was measured.

(ロ)試験区 表−7:試験A 表−8:試験B 注)混合施用した土壌改良剤 のpH(H2O)・曲・・・・10.6(2)試験の結
果 調査日ごとのpHの変化は次のとおりである。
(B) Test area Table-7: Test A Table-8: Test B Note) pH of the mixed applied soil conditioner (H2O) / 10.6 (2) Test results pH by survey date The changes are as follows.

表−9:試験A 表−10:試験B 上記試験結果かられかるように、本発明の土壌改良剤を
腐植質火山灰土及び硬質酸性土壌に施用した結果、本発
明による土壌改良剤は両土壌に対し酸度矯正効果のある
ことが認められた。
Table-9: Test A Table-10: Test B As can be seen from the above test results, the soil conditioner of the present invention was applied to humic volcanic ash soil and hard acidic soil. It was recognized that it has an acidity correction effect.

植物には最適pH領域があり、例えばエントウ、サトウ
キビ、ホウレンソウなどはpH6,5〜7.0、アスパ
ラガス、インゲン、オオムギ、カポチャ、カリフラワー
、カンビョウ、キュウーリ、コムギ、サトイモ、スイカ
、ハクサイ、ネギ、ナス、トマト、シュンキク、キク、
シクラメン等大部分の植物はpH6,0〜6.5、イネ
、キャベツ、ダイコン、コマツナなどはpH5,5〜6
.5、ウメ、ソバ、ラッキョウなどはpH5,5〜6.
0である。ところが、前記腐植質火山灰土壌はpH5,
5、硬質酸性土壌はpH5,0であり、殆んどの植物が
栽培困難であるが、本発明の土壌改良剤を施用すること
によって酸性土壌を植物栽培に最適な土壌に改良するこ
とができる。その施用量は目的とする植物及び適用土壌
に従って適宜の割合に容易に決定することができる。
Plants have an optimum pH range; for example, peas, sugar cane, and spinach have an optimum pH of 6.5 to 7.0, asparagus, green beans, barley, capocha, cauliflower, kambo, cucumber, wheat, taro, watermelon, Chinese cabbage, green onion, etc. Eggplant, tomato, chrysanthemum, chrysanthemum,
Most plants such as cyclamen have a pH of 6.0 to 6.5, while rice, cabbage, radish, Komatsuna, etc. have a pH of 5.5 to 6.
.. 5. Plum, buckwheat, rakkyo, etc. have a pH of 5.5-6.
It is 0. However, the humic volcanic ash soil has a pH of 5,
5. Hard acidic soil has a pH of 5.0, making it difficult to grow most plants; however, by applying the soil conditioner of the present invention, acidic soil can be improved into soil that is optimal for plant cultivation. The amount of application can be easily determined at an appropriate rate according to the target plant and the applied soil.

発明の効果 以上のように、本発明によれば、産業廃棄物である建設
汚泥から、従来のそれに匹敵しあるいはそれ以上の土壌
改良及び植物生育効果を有する土壌改良剤が得られる。
Effects of the Invention As described above, according to the present invention, a soil conditioner having soil improvement and plant growth effects comparable to or better than conventional ones can be obtained from construction sludge, which is industrial waste.

しかも、その原料は産業廃棄物である建設汚泥であるか
ら、極めて安価に製造できると共に、省資源の見地から
もまた産業廃棄物の処理上の面からも、極めて有用なも
のである。
Furthermore, since the raw material is construction sludge, which is industrial waste, it can be produced at an extremely low cost, and is extremely useful from the standpoint of resource conservation and industrial waste treatment.

【図面の簡単な説明】[Brief explanation of the drawing]

図面は本発明の方法の一実施態様を示す70−シートで
ある。
The drawing is a 70-sheet showing one embodiment of the method of the invention.

Claims (1)

【特許請求の範囲】[Claims] 建設汚泥を予備乾燥した後、造粒成型し、高温ガス接触
により焼成することを特徴とする建設汚泥から土壌改良
剤を製造する方法。
A method for producing a soil conditioner from construction sludge, which comprises pre-drying the construction sludge, granulating it, and calcining it by contact with high-temperature gas.
JP60041802A 1985-03-05 1985-03-05 Preparation of soil conditioner Granted JPS61203195A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60041802A JPS61203195A (en) 1985-03-05 1985-03-05 Preparation of soil conditioner

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60041802A JPS61203195A (en) 1985-03-05 1985-03-05 Preparation of soil conditioner

Publications (2)

Publication Number Publication Date
JPS61203195A true JPS61203195A (en) 1986-09-09
JPH045709B2 JPH045709B2 (en) 1992-02-03

Family

ID=12618462

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60041802A Granted JPS61203195A (en) 1985-03-05 1985-03-05 Preparation of soil conditioner

Country Status (1)

Country Link
JP (1) JPS61203195A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100694266B1 (en) * 2000-12-21 2007-03-14 재단법인 포항산업과학연구원 An apparatus and method for manufacturing organic fertilizer using sludge
JP2009132566A (en) * 2007-11-30 2009-06-18 Taiheiyo Material Kk Method of manufacturing porous sintered body
JP2010275343A (en) * 2009-05-26 2010-12-09 Kanto Kanzai:Kk Filter medium for soil improvement, method for manufacturing the filter medium for soil improvement, and method of soil improvement using the filter medium for soil improvement
JP2013177519A (en) * 2012-02-29 2013-09-09 Taisei Corp Liquid greening material and method for slope greening
JP2022097560A (en) * 2017-10-05 2022-06-30 国立研究開発法人理化学研究所 Reducer of irrigation water to plant, and method for reducing irrigation water to plant

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100694266B1 (en) * 2000-12-21 2007-03-14 재단법인 포항산업과학연구원 An apparatus and method for manufacturing organic fertilizer using sludge
JP2009132566A (en) * 2007-11-30 2009-06-18 Taiheiyo Material Kk Method of manufacturing porous sintered body
JP2010275343A (en) * 2009-05-26 2010-12-09 Kanto Kanzai:Kk Filter medium for soil improvement, method for manufacturing the filter medium for soil improvement, and method of soil improvement using the filter medium for soil improvement
JP2013177519A (en) * 2012-02-29 2013-09-09 Taisei Corp Liquid greening material and method for slope greening
JP2022097560A (en) * 2017-10-05 2022-06-30 国立研究開発法人理化学研究所 Reducer of irrigation water to plant, and method for reducing irrigation water to plant

Also Published As

Publication number Publication date
JPH045709B2 (en) 1992-02-03

Similar Documents

Publication Publication Date Title
BR112019026669A2 (en) mixture of polyalite and compacted potash and a process for producing the same
BR112020020079A2 (en) POLYHALITE AND POTASSA GRANULES
CN108300485A (en) It is a kind of to be used to administer the soil conditioner in salt-soda soil and its preparation method and application
US20210395158A1 (en) Compacted polyhalite and a process for the production thereof
CN103964918A (en) Long-acting organic-material compound fertilizer and preparation method
CN105001872A (en) Preparation method of soil conditioner taking phosphogypsum as raw material
CN109097052A (en) A kind of natural medical stone agricultural soil heavy metal deactivator and preparation method thereof
CN104962294A (en) Soil conditioner and preparation method thereof
CN103553845A (en) Technology for preparing soil loosening and adjusting fertilizer through treatment of grass carbon ash strong alkali wastewater in straw burning power plant
JPS61203195A (en) Preparation of soil conditioner
CN107056477A (en) For reducing conditioner of ammonia volatilization and preparation method thereof in Composting of Chicken Manure
KR100337084B1 (en) method for manufacturing compost by using sewage sluge
JP2017137203A (en) Siliceous fertilizer and manufacturing method therefor
KR101692825B1 (en) Artificial soil comprising dry bottom/middle ash and the manufacturing method of the same
JP2004329023A (en) Paddy-rice raising-seedling culture soil
JP2013032269A (en) Phosphate fertilizer and method for producing the same
JPH0236297A (en) Production of soil improving agent utilizing sludge
JPS5986687A (en) Preparation of zeolite-based soil conditioner from coal ash
CN110683885A (en) Coated slow-release fertilizer and application thereof in inhibiting absorption of heavy metal cadmium and reducing loss of nitrogen
KR100333773B1 (en) Soil improving product by means of gypsum and flyash and process
JPS593089A (en) Manufacture of organic fertilizer
CN106242890A (en) A kind of seaweed organic fertilizer
JP2012071994A (en) Method for promoting phosphate absorption by crop using sludge-fermented fertilizer and method for producing material for promoting phosphate absorption
JP2018043888A (en) Silicate fertilizer and production method thereof
JPH06279160A (en) Treatment of domestic animal excreta