JP2005126678A - Soil-improving material and method for improving soil by using the same - Google Patents

Soil-improving material and method for improving soil by using the same Download PDF

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JP2005126678A
JP2005126678A JP2004184685A JP2004184685A JP2005126678A JP 2005126678 A JP2005126678 A JP 2005126678A JP 2004184685 A JP2004184685 A JP 2004184685A JP 2004184685 A JP2004184685 A JP 2004184685A JP 2005126678 A JP2005126678 A JP 2005126678A
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soil
soil improvement
improving
improvement material
wood
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JP3711522B2 (en
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Hitomi Nakai
ひとみ 中井
Kunihiro Kawachi
邦弘 河地
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DAIKO KOGYO KK
ECO WORKS KK
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ECO WORKS KK
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    • 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
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    • Y02W30/78Recycling of wood or furniture waste

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Abstract

<P>PROBLEM TO BE SOLVED: To provide a material for improving soil by converting alkaline soil unsuitable for planting and not exhibiting humoral property into soil having a pH suitable for growing plants, and a method for improving the soil by using the same. <P>SOLUTION: The soil-improving material is provided by proliferating and preserving aerobic bacteria including alkaliphilic microorganisms or conditional anaerobic bacteria by using woody chips having ≤25 mm length including coarse woody chips having 7-25 mm length as culturing medium, and adding an activation-accelerating material. By mixing the soil-improving material with the highly alkaline soil to aim at the improvement of water permeability and water-holding property, the pH of the highly alkaline soil is lowered by utilizing the carbonatation by CO<SB>2</SB>exhausted by the respiration of the groups of microorganisms, and also the soil is changed by planting an alkali-loving plants as pioneer plants and utilizing a soil pH-improving effect by the plants. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

この発明は、植栽に不適な高アルカリ土壌で液性を示さない土壌を植物の生育に適したpHの土壌に改良するための土壌改良資材とそれを使った土壌改良方法である。   The present invention is a soil improvement material and a soil improvement method using the same for improving a soil having no pH in a highly alkaline soil unsuitable for planting into a soil having a pH suitable for plant growth.

近年、土木技術の進歩に伴い建設現場からベントナイトやセメントなどを含む高アルカリ土壌が大量に排出され、産業廃棄物であるが故にその廃棄処分方法が社会問題化している。また、造成工事等により露出した高アルカリ土壌に対する緑化植栽の困難さや、塩類集積により高アルカリ化した作土における栽培環境の悪化等が問題視されてきた。   In recent years, with the advancement of civil engineering technology, a large amount of highly alkaline soil including bentonite and cement has been discharged from construction sites, and since it is an industrial waste, its disposal method has become a social problem. In addition, difficulty in planting trees on highly alkaline soil exposed by the construction work, deterioration of cultivation environment in soil made highly alkaline by salt accumulation, and the like have been regarded as problems.

この対策として、硫酸塩資材(硫酸鉄、硫酸カリウムなど)、硫黄末や腐植酸の様な中和資材を混用するか、まさ土のような良質土や改良土壌を高アルカリ土壌の上に客土する手法が取られたり、微生物が創り出す有機酸による土壌の中和や、CO曝気による炭酸化での土壌改良等が研究されてきた。 As countermeasures, use a mixture of sulfate materials (iron sulfate, potassium sulfate, etc.), neutralizing materials such as sulfur powder and humic acid, or use high quality soil such as masato soil or improved soil on highly alkaline soil. Soil methods have been taken, soil neutralization with organic acids created by microorganisms, and soil improvement by carbonation by CO 2 aeration have been studied.

しかし、中和資材は流亡しやすく、短期間で効力をなくし、再び高アルカリ性を呈したり、大量の中和資材と労力が必要であるなどの問題があった。また、客土法も大量の良質土を必要とし、客土用土壌の採土地における新たな自然破壊が発生する。また、客土上に植物を植栽しても植物の生育と共に根がアルカリ土壌に達し、生育障害を起こす可能性が懸念される。同時にいずれの方法も工期の長さや、コスト高を免れない等の欠点があり、これら高アルカリ土壤の簡便で安価な改良法が切望されていた。
特開2003−265038 特開2000−136525 特開2000−41479 山田僚一、須藤芳雄、丸山俊朗 「濁水処理に伴う脱水ケーキの土壌緑化基盤材への改良に関する基礎的研究」 土木学会論文集VII 692巻21号 「建設汚泥の有効利用」 (財)先端建設技術センター(1998年)
However, the neutralizing material is easy to run away, and there is a problem that it becomes ineffective in a short period of time, becomes highly alkaline again, and requires a large amount of neutralizing material and labor. In addition, the Soil Law also requires a large amount of high-quality soil, and new natural destruction occurs in the land where the soil for the soil for use is collected. Moreover, even if a plant is planted on the soil, there is a concern that the root may reach alkaline soil with the growth of the plant and cause a growth failure. At the same time, each method has drawbacks such as a long construction period and high costs, and a simple and inexpensive improvement method for these high alkaline earths has been desired.
JP 2003-265038 A JP 2000-136525 A JP 2000-41479 A Ryoichi Yamada, Yoshio Sudo, Toshiro Maruyama “Fundamental study on improvement of dewatered cake to soil revegetation base material due to muddy water treatment” JSCE Proceedings VII 692 21 "Effective use of construction sludge" Advanced Construction Technology Center (1998)

そこでこの発明は、一般廃棄物である緑化樹木の剪定枝や刈り草等をはじめとする植物質を原材料にした木質チップを培養基材とし、天然に存在し好アルカリ性を示す糸状菌、細菌、放線菌などの好気性および条件的嫌気性菌群を含む微生物群を大量に培養し、活性度を上げたこれら微生物群を、高アルカリ土壌と混合することにより微生物の呼吸で発生するCOによる炭酸化の力で土壌pHを低下させることを課題とする。 Therefore, the present invention uses, as a culture substrate, wood chips made from plant materials such as pruned branches and cut grass of green trees that are general wastes, and is a naturally occurring filamentous fungus, bacteria, By culturing a large number of microorganisms including aerobic and conditional anaerobic bacteria such as actinomycetes, and increasing the activity of these microorganisms by mixing with highly alkaline soil, CO 2 generated by respiration of microorganisms It makes it a subject to reduce soil pH by the power of carbonation.

以上の課題を解決するために、第一発明は天然に存在する好アルカリ性微生物群を多く含む微生物群を選抜し、これら微生物群が発生させるCOによる炭酸化を利用し高アルカリ土壌のpHを低下させ、植栽に適した土壌に変えることを特徴とする土壌改良資材の発明である。 In order to solve the above problems, the first invention were selected microorganisms rich in alkalophilic microorganisms naturally occurring, the pH of utilizing carbonated by CO 2 that these microorganisms can cause highly alkaline soils It is invention of the soil improvement material characterized by reducing and changing to the soil suitable for planting.

第二発明は一般廃棄物である緑化樹木の剪定枝や刈り草等を原材料とし、長さ7〜25mmの木質粗大チップを10〜40%、好ましくは20〜30%含む長さ25mm以下の木質チップを、高アルカリ土壌に混合し、土壌の物理性である通気性および透水性を改良させる。木質粗大チップ含有率が10%以下では透水性が改良されず、40%以上では微生物の活性が劣るため、この範囲内が最適である。この木質粗大チップの働きにより送気、曝気等の特別な手段をとることなく土壌中への空気の供給を増し、微生物群の活性化を図ることができる。活性化した微生物群が発生するCOにより土壌pHを低下させ、液性を示さない建設汚泥、建設残土などの高アルカリ土壌を、環境省令で定める排水基準であるpH8.6以下の植栽土壌に改良することを特徴とする土壌改良資材の発明である。 The second invention uses pruned branches, cut grass, etc. of greening trees, which are general wastes, as raw materials, and wood quality of 25 mm or less containing 10 to 40%, preferably 20 to 30%, of woody coarse chips of 7 to 25 mm in length. Chips are mixed into highly alkaline soils to improve the physical and breathability of the soil. If the woody coarse chip content is 10% or less, the water permeability is not improved, and if it is 40% or more, the activity of microorganisms is inferior. The action of the woody large chip can increase the supply of air into the soil without taking special measures such as air supply and aeration, and can activate the microorganism group. The CO 2 that activated microorganisms occurs lowering the soil pH, construction sludge that does not exhibit a humoral, a highly alkaline soils and construction waste soil, pH 8.6 following planting soil is drained standards specified by the Ordinance of the Ministry of the Environment It is the invention of the soil improvement material characterized by improving to.

また、第三発明は好アルカリ性糸状菌・細菌・放線菌等を含む微生物群を木質チップからなる培養基材を用いて培養し、COを大量にしかも2箇月以上にわたって発生するよう活性化させた土壌改良資材を土壌に混合し、土壌pHを改良するものである。 Further, the third invention is a method of culturing a group of microorganisms containing alkalophilic filamentous fungi, bacteria, actinomycetes, etc. using a culture substrate comprising a wood chip and activating it to generate CO 2 in large quantities and over 2 months. The soil improvement material is mixed with the soil to improve the soil pH.

第四発明は土壌改良資材を土壌に混合する直前に、その微生物群が発生するCO濃度が1〜15%、好ましくは5〜10%まで上昇させ、しかもCOの発生を2箇月以上持続させ、炭酸化能力を最大限に発揮させることの可能な易分解性有機物を主とした活性化促進資材を使用することによる土壌改良法の発明である。 In the fourth invention, immediately before mixing the soil improvement material with the soil, the CO 2 concentration generated by the microorganism group is increased to 1 to 15%, preferably 5 to 10%, and the generation of CO 2 is continued for 2 months or more. It is an invention of a soil improvement method by using an activation promoting material mainly composed of an easily decomposable organic substance capable of maximizing the carbonation ability.

第五発明は前記土壌改良剤を、液性を示さない高アルカリ土壌に混合し、活性化した微生物群が発生するCOの炭酸化により高アルカリ土壌のpHを低下させる土壌改良法で、土壌混合後に曝気や土壌の撹拌など、特別な操作を伴わないことを特徴とする土壌改良法の発明である。 The fifth invention of the soil improving agent, and mixed in a high alkaline soil showing no liquid, in activated soil improvement method for reducing the pH of the highly alkaline soils by carbonation of CO 2 microorganisms occurs with soil It is an invention of a soil improvement method characterized by no special operations such as aeration and soil agitation after mixing.

本発明によれば、一般廃棄物と見なされる剪定枝や刈り草等を活用し、産業廃棄物である建設汚泥や、土壌改良が必要とされる高アルカリ土壌の改良が簡単に行なえる。このことにより、例えば産業廃棄物として厄介者扱いされる建設汚泥でさえも植栽土壌として利用が可能であり、かつpH値が8.6以下となることから従来の建設汚泥や建設汚泥改良土を使った造成工事の際に必要であった排水処理施設も不要となる。   According to the present invention, it is possible to easily improve construction sludge, which is industrial waste, or highly alkaline soil that requires soil improvement, using pruned branches, cut grass, and the like that are regarded as general waste. As a result, for example, even construction sludge treated as a nuisance as industrial waste can be used as planting soil, and since the pH value is 8.6 or less, conventional construction sludge and construction sludge improved soil The wastewater treatment facility that was necessary for the construction work using the slab is no longer necessary.

この発明の実施形態は、活性化された好アルカリ性微生物群を含む土壌改良資材を高アルカリ土壌へ混合することであり、微生物群が活性化されていない場合にはpH値を短期間に8.6程度まで下げることは困難である。   Embodiment of this invention is mixing the soil improvement material containing the activated alkaliphilic microorganisms to a highly alkaline soil, and when microorganisms are not activated, pH value is set to 8. It is difficult to lower it to about 6.

本発明の基礎原理はCOガスが水に溶けCa(OH)と反応し炭酸カルシウムとなってpHを低下させる炭酸化の応用である。 The basic principle of the present invention is the application of carbonation in which CO 2 gas dissolves in water and reacts with Ca (OH) 2 to form calcium carbonate and lower the pH.

CO濃度は、通常大気中では0.03%程度である。また、コンポスト堆肥は0.1%〜0.5%程度である。しかし、本発明による土壌改良資材では、最大値ではあるが、驚くべきことに通常大気の150〜300倍に、しかも2箇月以上の長期間にわたり高濃度のCOが放出され続ける。この条件が満たされない場合、当初の目的を達成することは困難である。 The CO 2 concentration is usually about 0.03% in the atmosphere. Compost compost is about 0.1% to 0.5%. However, in the soil improvement material according to the present invention, although it is the maximum value, surprisingly, a high concentration of CO 2 continues to be released over 150 to 300 times the normal atmosphere over a long period of two months or more. If this condition is not met, it is difficult to achieve the original objective.

本発明における微生物群の培養基材として、長さ7〜25mmの木質粗大チップを容積比10〜40%、好ましくは20〜30%含む、長さ25mm以下の木質チップを用いる。このことは通気性、透水性および保水性などの土壌物理性改良に有効である。これらの土壌物理性の改良が本発明による土壌改良資材を構成する微生物群に必要な空気を供給し、必要水分も保持し微生物群の活性化に結びついている。従って、培養基材は上記長さの粗大チップを含むものでなければならない。   As a culture substrate for the microorganism group in the present invention, a wood chip having a length of 25 mm or less containing a wood coarse chip having a length of 7 to 25 mm in a volume ratio of 10 to 40%, preferably 20 to 30% is used. This is effective for improving soil physical properties such as air permeability, water permeability and water retention. These improvements in the physical properties of the soil supply necessary air to the microorganism group constituting the soil improvement material according to the present invention, hold the necessary moisture, and lead to the activation of the microorganism group. Therefore, the culture substrate must contain coarse chips of the above length.

剪定枝を含む木質チップは通常C/N比100以上であり、この数値は容易に発酵を完了し得ないことを意味している。つまり、微生物の増殖が長期間にわたり持続されることを意味し、バーク堆肥等で問題となる急激な窒素飢餓も比較的起こりにくい。   Wood chips containing pruned branches usually have a C / N ratio of 100 or more, and this figure means that fermentation cannot be completed easily. In other words, it means that the growth of microorganisms is sustained over a long period of time, and sudden nitrogen starvation which is a problem in bark compost or the like is relatively difficult to occur.

また、木質チップで培養された微生物群は常に環境の影響を受けその活性度が変化している。木質チップでの培養過程では初期には好気性微生物群(絶対好気性菌群等)が多量の酸素と有機物を得て活性化するが、やがて条件的嫌気性菌群が主流となる。この好気性微生物群と条件的嫌気性菌群の活性を長期間持続するように調整したものが土壌改良資材である。   In addition, the microorganism group cultured on the wood chip is always affected by the environment and its activity changes. In the cultivation process using wood chips, initially, aerobic microorganisms (absolute aerobic bacteria, etc.) are activated by obtaining a large amount of oxygen and organic matter, but eventually, conditional anaerobic bacteria become mainstream. A soil improvement material is prepared by adjusting the activities of the aerobic microorganism group and the conditional anaerobic bacteria group for a long period of time.

培養の極く初期には、土壌改良資材の原材料に含まれる有害病原菌や害虫類が生存し、かつ、酸素不足から嫌気発酵をおこしやすく、その結果植物に有害なフェノール性酸が発生、残存し、植物の生育に悪影響をもたらすことが多い。これを回避するため培養は通気、通水に注意を図りながら好気的に進める必要がある。その間に60〜70℃の発酵温度を1週間程度保ち、有害病原菌や害虫類の死滅を図らねばならない。   At the very beginning of the cultivation, harmful pathogens and pests contained in the raw materials of the soil amendment materials survive, and are susceptible to anaerobic fermentation due to lack of oxygen. As a result, phenolic acids harmful to plants are generated and remain. Often has a negative effect on plant growth. In order to avoid this, it is necessary to proceed aerobically while paying attention to aeration and water flow. In the meantime, the fermentation temperature of 60 to 70 ° C. must be maintained for about one week to kill harmful pathogens and pests.

その後、好アルカリ性好気性微生物群と好アルカリ性条件的嫌気性菌群が中心となった発酵に移るが、この状態で保存したものあるいはこの状態に至ったものに活性化促進資材を添加し、高アルカリ土壌に混用することで高アルカリ土壌のpHを低下させることができる。   After that, the fermentation process centered on the aerobic aerobic microorganism group and the aerobic conditional anaerobic bacteria group was added. By mixing with alkaline soil, the pH of highly alkaline soil can be lowered.

本発明による土壌改良資材の土壌への混合割合は、容積比で土壌の20%〜50%である。この比率は、改良を必要とする土壌のpH値に応じて変えるのがよい。例えば、pH9程度の建設汚泥であれば20%で充分であるが、pH12程度の場合には30%以上が適量である。   The mixing ratio of the soil improving material according to the present invention to the soil is 20% to 50% of the soil in volume ratio. This ratio should be varied according to the pH value of the soil in need of improvement. For example, 20% is sufficient for construction sludge having a pH of about 9, but 30% or more is appropriate for a pH of about 12.

木質チップは、元来、それ自体に微生物が大量に増殖しており微生物群の構成種や活性度は常に変化しているものである。本発明では、高アルカリ土壌に直接、土壌改良資材を混入する為、施用された微生物群は高アルカリ性の環境下で十分活性化出来なければならない。   Wood chips originally have a large number of microorganisms growing themselves, and the constituent species and activity of the microorganism group are constantly changing. In the present invention, since the soil improvement material is mixed directly into the highly alkaline soil, the applied microorganism group must be able to be sufficiently activated in a highly alkaline environment.

そのため、多数の試作改良資材の中から、高アルカリ性土壌の中で活性度の高い微生物群を選抜した。この微生物群を種菌として経代培養し本発明の土壌改良資材に植菌培養し用いるものである。   Therefore, a group of microorganisms with high activity in high alkaline soil was selected from a large number of trial improvement materials. This microorganism group is subcultured as an inoculum and inoculated and used as the soil improvement material of the present invention.

しかし、種菌を経代培養することは非実用的であるため、実用化に際し常時は休眠状態におき、必要なときに活性化させる方法を見出した。それは微生物の活動と水分の関係を探求した結果、含水量(圃場容水量に対する重量比)30%以下とし、降雨による透水を避ける方法で貯蔵することでほぼ休眠状態とすることが出来たのである。   However, since it is impractical to cultivate the inoculum, it has been found that there is a method in which the inoculum is always in a dormant state and activated when necessary. As a result of investigating the relationship between the activity of microorganisms and moisture, the water content (weight ratio to the field water content) was 30% or less, and it was possible to make it almost dormant by storing it in a way that avoids water permeability due to rainfall. .

ここで、含水量は2mmの篩でふるい落とした試料を用い、新たに見出した土壌改良資材用検量線をインプットした水分計を用いて測定した圃場容水量に対する比率である。   Here, the water content is a ratio with respect to the field water capacity measured using a moisture meter to which a new calibration curve for soil improvement materials was input using a sample screened off with a 2 mm sieve.

本法による土壌改良では、PHを8.5以下に下げるには若干の期間を要する。この対策としてセスバニアのような耐アルカリ性植物(パイオニア植物)を栽培し、土壌の中性化を促進すれば期間短縮が可能である。   In soil improvement by this method, it takes some time to lower PH to 8.5 or less. As a countermeasure, it is possible to shorten the period by cultivating an alkali-resistant plant (pioneer plant) such as Sesbania and promoting neutralization of soil.

以下に実施例を示して、本発明を具体的に説明するが、本発明を限定するものではない。   EXAMPLES The present invention will be specifically described below with reference to examples, but the present invention is not limited thereto.

活性度の異なる木質チップから成る土壌改良資材を、容積比30%の比率で、高アルカリ土壌に混合したところ、その中の活性度1.6を有する土壌改良資材が当初pH11.1であった高アルカリ土壌をpH8.6まで低下させる事実が見出された。これは既存技術でなし得なかった技術である。この際のpH変化を図1および図2に示した。図中(1)は比較例で建設汚泥そのもの、(2)は実施例で建設汚泥に土壌改良資材30%添加した例である。混用8日後または10日後で、(1)比較例でのpHは土壌で10.0以上、浸出液で9.5以上を維持したが(2)実施例ではそれぞれpH8.5および8.4となった。   When soil improvement materials composed of wood chips with different activities were mixed with high alkaline soil at a volume ratio of 30%, the soil improvement material having an activity of 1.6 was initially pH 11.1. The fact was found that the highly alkaline soil was lowered to pH 8.6. This is a technology that could not be achieved with existing technology. The pH change at this time is shown in FIG. 1 and FIG. In the figure, (1) is a comparative example of construction sludge itself, and (2) is an example of adding 30% soil improvement material to construction sludge in the example. 8 or 10 days after mixed use (1) The pH in the comparative example was maintained at 10.0 or higher in the soil and 9.5 or higher in the leachate, but (2) in the examples, the pH was 8.5 and 8.4, respectively. It was.

ここで、活性度は土壌改良資材3.7リットルを特製ガラス容器(8リットル)に入れ、150分後のCO濃度をガス検知管で測定し、この測定値(%)で判断した。また、土壌pHは試料10gに蒸留水50gを加え撹拌後、1時間静置した後自動温度補償装置付きpH計で測定し、浸出水pHは、45型プランターに入れた土壌10リットルに蒸留水1リットルを潅注し、プランターの底部へ浸出した水のpHを測定した。 Here, 3.7 liters of soil improvement material was put into a special glass container (8 liters), and the CO 2 concentration after 150 minutes was measured with a gas detector tube, and the activity was judged by this measured value (%). The soil pH was determined by adding 50 g of distilled water to 10 g of the sample, stirring, and allowing to stand for 1 hour, and then measuring with a pH meter with an automatic temperature compensator. The leachate pH was determined by adding distilled water to 10 liters of soil in a 45-type planter. One liter was irrigated and the pH of the water leached to the bottom of the planter was measured.

休眠状態の微生物を含む土壌改良資材に、活性化促進資材として植物油搾油残渣、精糖廃蜜、豆乳絞り粕、キノコ培地、乾燥鶏糞、硫安および尿素を土壌改良資材に添加したところ、植物油搾油残渣を1%添加した土壌改良資材のCO発生量は5.6%に達した。添加量を4%まで増した区では、COよりもアンモニアガスの発生が多く見られた。従って、活性化促進資材の添加量は1〜2%が適量と考えられた。 When soil-improvement materials containing dormant microorganisms were added to the soil-improving material, vegetable oil residue, refined sugar beet, soymilk pomace, mushroom medium, dried chicken manure, ammonium sulfate, and urea were added to the soil-improving material. The amount of CO 2 generated by the soil improvement material added by 1% reached 5.6%. In the section where the addition amount was increased to 4%, more ammonia gas was generated than CO 2 . Therefore, it was considered that the addition amount of the activation promoting material was 1 to 2%.

尿素は窒素濃度が高く、急激なアンモニアガスの発生を認めたが、CO発生量は少なく本発明に必要な条件を満たさなかった。活性化促進資材によっては添加直後のCO発生量は順調であるが持続性の劣るものや、初期のCO発生量は多くないが長期にわたって発生するものなどがあり、状況に合わせて脂肪分やタンパク質、炭水化物などを含む活性化促進資材を選択するのが良い。結果を表1に示した。 Urea has a high nitrogen concentration and a rapid generation of ammonia gas was observed, but the amount of CO 2 generated was small and did not satisfy the conditions required for the present invention. Depending on the activation-promoting material, the amount of CO 2 generated immediately after addition is satisfactory, but the sustainability is inferior, and the initial CO 2 generation amount is not large, but it is generated over a long period of time. It is recommended to select an activation promoting material including protein, protein and carbohydrate. The results are shown in Table 1.

* 添加活性化促進資材中のN重量g/土壌改良資材1kg
表1 活性化促進資材の添加によるCO発生量
* N weight g in additive activation promotion material / 1kg soil improvement material
Table 1 CO 2 emissions due to the addition of activation promoting materials

土壌改良資材を、雨水の浸透を避けながら保存し供試した。加水量を変えながら微生物の活性度をCO濃度で調べたところ、含水量30%以下であれば微生物は6箇月以上ほぼ休眠状態にあることが判明した。このことは含水量30%以下で保存した試料に加水し、活性化させ種菌群として使用出来ることを意味している。結果を図3に示した。 The soil improvement material was preserved and tested while avoiding the infiltration of rainwater. As a result of examining the activity of the microorganism by CO 2 concentration while changing the amount of water added, it was found that if the water content was 30% or less, the microorganism was almost dormant for 6 months or more. This means that it can be used as an inoculum group by hydrating and activating a sample stored at a water content of 30% or less. The results are shown in FIG.

保存中の土壌改良資材を使用し、実際の現場における土壌改良方法の検討を行った。まず、土壌改良資材として休眠中の微生物群を活性化するため、次の方法で休眠打破を行った。すなわち、土壌改良資材の含水量を70%に調整し活性化促進資材を重量比で2%添加した。この結果、保存時CO濃度0.3%であったものが供試時には5.2%まで活性化した。 We examined soil improvement methods at actual sites using soil improvement materials during storage. First, in order to activate a dormant microorganism group as a soil improvement material, the dormancy was broken by the following method. That is, the moisture content of the soil improvement material was adjusted to 70%, and the activation promoting material was added by 2% by weight. As a result, the CO 2 concentration at the time of storage of 0.3% was activated to 5.2% at the time of test.

この土壌改良資材を、pH12.0の高アルカリ性建設汚泥+建設残土に容積比で30%混合し高麗芝、洋芝(トールフェスク)、緑肥作物(セスバニア)を植付けまたは播種し、その後の土壌、浸出水のpH変化と作物の生育状況を調査し、結果を図4乃至図6に示した。図中、1(建設汚泥)および2(建設汚泥+建設残土)は比較例であり、3(建設汚泥+建設残土+土壌改良資材)および4(建設汚泥+建設残土+土壌改良資材+粒状基盤)は実施例である。調査は、2003年5月20日から同年8月30日まで実施した。処理後の土壌のpH変化を図4に示した。土壌pHは各試験区の5箇所からそれぞれ深さ5cmの土壌を採土し混合した試料10gに蒸留水50gを加え、撹拌後1時間静置した後、自動温度補償装置付きpH計で測定した。その結果、土壌pHは供試直後から低下し、供試約2箇月後には排出基準を満たすpH8.6にまで低下した。   This soil improvement material is mixed with high alkaline construction sludge of pH 12.0 + construction residual soil at a volume ratio of 30%, and planted or seeded with ginseng grass, turf (tall fescue), green manure crop (sesbania), and then the soil, leaching Changes in water pH and crop growth were investigated, and the results are shown in FIGS. In the figure, 1 (construction sludge) and 2 (construction sludge + construction residual soil) are comparative examples, 3 (construction sludge + construction residual soil + soil improvement material) and 4 (construction sludge + construction residual soil + soil improvement material + granular foundation) ) Is an example. The survey was conducted from May 20, 2003 to August 30, 2003. The change in pH of the soil after the treatment is shown in FIG. The soil pH was measured with a pH meter equipped with an automatic temperature compensation device after adding 50 g of distilled water to 10 g of a sample obtained by collecting and mixing soil having a depth of 5 cm from five locations in each test section, and stirring for 1 hour after stirring. . As a result, the soil pH decreased immediately after the test, and decreased to pH 8.6 that satisfied the discharge standard after about two months of the test.

図5には浸出水pHの推移を示した。浸出水は各試験区の5箇所からそれぞれ深さ5〜10cmの土壌を採土し混合した試料をφ125mmの塩ビ管に高さ20cmまで詰め、上部より1000ccの蒸留水を加え、底部からの浸出水のpHを測定した。その結果、供試2箇月後にはpHは8.5以下に下がった。   FIG. 5 shows the transition of the leachate pH. For the leachate, 5 to 10 cm depth of soil was collected from 5 locations in each test zone, and the mixed sample was packed in a φ125 mm PVC pipe to a height of 20 cm, 1000 cc of distilled water was added from the top, and leaching from the bottom. The pH of the water was measured. As a result, the pH dropped to 8.5 or less after 2 months of the test.

図6には、洋芝(トールフェスク)の刈芝重量累積値を示した。約2箇月の結果ではあるが、土壌改良した実施例の刈芝重量が比較例を上回ることが明確となった。   FIG. 6 shows the cumulative value of the cut grass weight of the turf (tall fescue). Although it was a result of about 2 months, it became clear that the weight of the cut grass of the example which improved the soil exceeded the comparative example.

土壌改良資材を混合して1〜2箇月経過後の土壌は、pH8.6前後で植栽土壌としては若干pHが高すぎる場合もある。そこで、このような土壌での栽培可能な植物種の確認試験を実施した。その結果、土壌改良直後には芝生ではトールフェスク、ペレニアルライグラス、バミューダグラス、コウライシバなどの耐アルカリ性植物の生育がよく、緑肥植物ではセスバニア、クロタラリア、ソルゴー、エンバク、アルファルファなどが好成績を収めた。   The soil after mixing with soil improvement materials and after a lapse of 1 to 2 months may have a pH that is slightly too high as a planting soil at around pH 8.6. Then, the confirmation test of the plant species which can be grown in such a soil was implemented. As a result, immediately after soil improvement, alkali-tolerant plants such as tall fescue, perennial ryegrass, bermudagrass, and kobashishiba grew well on the lawn, and sesbania, crotalaria, solgo, oat, alfalfa, etc. achieved good results for green manure plants.

緑肥植物の一つであるセスバニアの生育状況を、図7に示した。セスバニアの播種は2003年5月27日、刈り取りは同年9月1日に実施した。試験開始3ヵ月後(2003年9月3日)の調査ではあるが、建設汚泥におけるトールフェスク植栽区の土壌pHは11.0であったが、セスバニア区では9.9〜8.5であることから、セスバニア自身も土壌のpH改良効果を有することがわかった。このことからセスバニアなどの土壌pH改良効果を有する植物を土壌改良植物として選択し、それら作物による改良効果をも活用するのが良い。   The growth situation of Sesbania, one of the green manure plants, is shown in FIG. Sesbania was sowed on May 27, 2003, and mowing was conducted on September 1, 2003. Although it is a survey three months after the start of the test (September 3, 2003), the soil pH of the tall fescue planting zone in the construction sludge was 11.0, but in the Sesbania district it is 9.9 to 8.5. From this, it was found that Sesbania itself has an effect of improving soil pH. Therefore, it is preferable to select a plant having a soil pH improving effect, such as sesbania, as a soil improving plant, and to make use of the improving effect of these crops.

同時に土壌中でのCOの発生状況を調べた。その結果を図8に示したが、混合後9箇月を経過しているにもかかわらず、土壌改良資材混合区では高いCO濃度を確認した。比較例の建設汚泥区および建設汚泥+残土区ではほとんどCOが検知されなかった。
[他の実施形態]
At the same time, the occurrence of CO 2 in the soil was examined. The results are shown in FIG. 8, and a high CO 2 concentration was confirmed in the soil-improving material mixed section even though 9 months had passed after mixing. In the comparative construction sludge zone and construction sludge + residual soil zone, almost no CO 2 was detected.
[Other Embodiments]

実施例では、木質チップの原料として剪定枝を粉砕したものを用いたが、他の実施形態では建設廃材、ヤシガラ種皮などでも良い。また、発酵時の水分、窒素等の補充として植物質または、および家畜糞尿の利用も出来る。   In the examples, the crushed pruned branches were used as the raw material for the wood chips. However, in other embodiments, construction waste, coconut seed coats, etc. may be used. In addition, plant material or livestock manure can be used as a supplement for moisture and nitrogen during fermentation.

活性化促進資材としては植物油搾油残渣が最も良い結果を得たが、使用濃度などを調整することでその他の低分子の糖類やタンパク質、アミノ酸などの易分解性有機物等が利用可能である。   As an activation promoting material, vegetable oil extraction residue has obtained the best results, but other low molecular sugars, proteins, amino acids and other readily decomposable organic substances can be used by adjusting the concentration used.

本発明になる微生物群は、好アルカリ性微生物群を含み、好気性微生物群または、および条件的嫌気性菌群であればその種類を問わない。しかし、自然状態では好アルカリ性微生物群が少ない場合もあり、発酵を促進する為、保存微生物群の一部を種菌として木質培養基材に添加するとなおよい結果が得られる。   The microorganism group according to the present invention includes an aerobic microorganism group, and any type of aerobic microorganism group or a conditional anaerobic bacteria group may be used. However, there are cases where the number of alkalophilic microorganisms is small in the natural state, and in order to promote fermentation, better results can be obtained by adding a part of the preserved microorganisms as a seed fungus to the woody culture substrate.

本発明では、補助的に高アルカリ土壌のpHを改良する植物としてセスバニアを示したが、栽培することで土壌pHを下げる働きのある耐アルカリ性植物であればその種類を問わない。   In the present invention, Sesbania has been shown as a plant that supplementarily improves the pH of highly alkaline soil, but any type of plant can be used as long as it is an alkali-tolerant plant that has a function of lowering soil pH by cultivation.

建設汚泥の廃棄処分は、その方法、場所、経費の点で大きな社会問題であり適正な処理が困難なことから不法投棄を引き起こすことにもなる。したがって、これら建設汚泥を植栽土壌として再利用することは今日の建設業界の課題であり、その解決策として本発明が活用できる。   The disposal of construction sludge is a major social problem in terms of its method, location, and cost, and it causes illegal dumping because it is difficult to properly treat. Therefore, reusing these construction sludge as planting soil is a problem for today's construction industry, and the present invention can be utilized as a solution.

樹木剪定枝は一般廃棄物として扱われ、これも焼却に多大の費用を費やしているのが現状である。従って、樹木剪定枝を土壌改良資材の木質培養基材の一つとして用いる場合は、廃棄物の再利用として有益である。 Tree pruned branches are treated as general waste, and the current situation is that they also spend a great deal of money on incineration. Therefore, when the tree pruned branch is used as one of the woody culture base materials for the soil improvement material, it is useful as a waste recycling.

本発明による土壌改良資材による改良土の土壌pH変化Change of soil pH of improved soil by soil improving material according to the present invention 本発明による土壌改良資材による改良土の浸出液pH変化PH change in leachate of improved soil by soil improvement material according to the present invention 土壌改良資材の含水率と炭酸ガス発生量Water content and carbon dioxide generation amount of soil improvement materials 本発明による土壌改良資材の実証試験(土壤pH改良結果)Demonstration test of soil improvement material according to the present invention (result of soil pH improvement) 本発明による土壌改良資材の実証試験(浸出水pH改良結果)Demonstration test of soil improvement material according to the present invention (leachate pH improvement result) 本発明による土壌改良資材の実証試験(トールフェスク刈芝生草重)Demonstration test of soil improvement material according to the present invention (tall fescue grass lawn weight) 本発明による土壌改良資材の実証試験(セスバニア生草重)Demonstration test of soil improvement material according to the present invention (Sesbania fresh grass weight) 本発明による土壌改良資材の実証試験(9箇月後のCO発生量)Demonstration test of soil improvement material according to the present invention (CO 2 generation amount after 9 months)

Claims (6)

木質粗大チップと木質培養基材で培養した好アルカリ性微生物である糸状菌、細菌および放線菌等の微生物群を含む土壌改良資材であって、高アルカリ土壌の通気性、透水性および保水性を改良し、土壌pHを低下させ、植栽に適した土壌に変えることを特徴とする土壌改良資材。 A soil improvement material containing microorganisms such as filamentous fungi, bacteria, and actinomycetes, which are alkalophilic microorganisms cultivated on coarse wood chips and wood culture substrates, improving the air permeability, water permeability and water retention of highly alkaline soils A soil improvement material characterized by lowering the soil pH and changing to soil suitable for planting. 前記の土壌改良資材は長さ7〜25mmの木質粗大チップを含み、この粗大チップが土壌の通気性および透水性を改良し、木質培養基材としては微生物群の活性を長期間持続させ、7mm以下の木質チップが微生物群の初期活性を促す木質培養基材として働くことを特徴とする請求項1記載の土壌改良資材。 The soil improvement material includes a woody coarse chip having a length of 7 to 25 mm. The coarse chip improves the air permeability and water permeability of the soil, and the activity of the microorganism group as a woody culture substrate is maintained for a long period of time. The soil improvement material according to claim 1, wherein the following wood chip serves as a wood culture substrate that promotes the initial activity of the microorganism group. 前記木質粗大チップと木質チップの比率として、木質粗大チップを容積比で10〜40%、好ましくは20〜30%含むことを特徴とする請求項1および請求項2に記載の土壌改良資材。 3. The soil improvement material according to claim 1, wherein the ratio of the wood coarse chip to the wood chip is 10 to 40%, preferably 20 to 30% of the wood coarse chip in a volume ratio. 前記微生物群は高濃度のCOを2箇月以上にわたり発生し続ける微生物群を含むことを特徴とする請求項1乃至請求項3に記載の土壌改良資材。 The soil improvement material according to any one of claims 1 to 3, wherein the microorganism group includes a microorganism group that continuously generates a high concentration of CO 2 for two months or more. 前記微生物群による炭酸化能力を最大限に発揮させる為に、高濃度のCOを発生させ得る活性化促進資材を混合することを特徴とする請求項1乃至請求項4に記載の土壌改良資材。 The soil improvement material according to any one of claims 1 to 4, wherein an activation promoting material capable of generating a high concentration of CO 2 is mixed in order to maximize the carbonation ability of the microorganism group. . 請求項1乃至請求項5に記載の土壌改良資材を高アルカリ土壌に混合することにより植栽に適した土壌に改良することを特徴とする土壌改良方法。
The soil improvement method characterized by improving to the soil suitable for planting by mixing the soil improvement material of Claim 1 thru | or 5 with highly alkaline soil.
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CN103484128B (en) * 2013-08-29 2015-07-29 南京农业大学 A kind of alkaline land modifying agent and preparation method thereof and application thereof
CN104686186A (en) * 2015-04-02 2015-06-10 张玉雯 Method for cultivating corn in saline-alkali soil
CN114698425A (en) * 2022-03-16 2022-07-05 临沂大学 Method for rapidly improving agricultural soil fertility
CN114698425B (en) * 2022-03-16 2023-09-29 临沂大学 Method for rapidly improving soil fertility of agricultural soil

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