JP2006265504A - Hardening material containing charcoal - Google Patents
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- JP2006265504A JP2006265504A JP2005090000A JP2005090000A JP2006265504A JP 2006265504 A JP2006265504 A JP 2006265504A JP 2005090000 A JP2005090000 A JP 2005090000A JP 2005090000 A JP2005090000 A JP 2005090000A JP 2006265504 A JP2006265504 A JP 2006265504A
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- 239000000463 material Substances 0.000 title claims abstract description 101
- 239000003610 charcoal Substances 0.000 title claims abstract description 62
- 239000002689 soil Substances 0.000 claims abstract description 155
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims abstract description 109
- 239000000395 magnesium oxide Substances 0.000 claims abstract description 53
- 239000003337 fertilizer Substances 0.000 claims abstract description 32
- 239000003513 alkali Substances 0.000 claims abstract description 22
- 239000000203 mixture Substances 0.000 claims abstract description 20
- 238000007711 solidification Methods 0.000 claims description 18
- 230000008023 solidification Effects 0.000 claims description 18
- 239000002440 industrial waste Substances 0.000 claims description 16
- 238000004519 manufacturing process Methods 0.000 claims description 15
- 239000010871 livestock manure Substances 0.000 claims description 8
- 239000002023 wood Substances 0.000 claims description 8
- 235000007164 Oryza sativa Nutrition 0.000 claims description 5
- 235000009566 rice Nutrition 0.000 claims description 5
- 239000003245 coal Substances 0.000 claims description 4
- 235000013305 food Nutrition 0.000 claims description 4
- 239000010903 husk Substances 0.000 claims description 4
- 239000000470 constituent Substances 0.000 claims description 2
- 238000012272 crop production Methods 0.000 claims description 2
- 240000007594 Oryza sativa Species 0.000 claims 1
- 238000003756 stirring Methods 0.000 claims 1
- 239000010802 sludge Substances 0.000 abstract description 11
- 230000009467 reduction Effects 0.000 abstract description 4
- 238000009423 ventilation Methods 0.000 abstract description 4
- 238000004140 cleaning Methods 0.000 abstract 1
- 230000000694 effects Effects 0.000 description 23
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 14
- 235000011941 Tilia x europaea Nutrition 0.000 description 14
- 239000004571 lime Substances 0.000 description 14
- 235000019645 odor Nutrition 0.000 description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 12
- 239000004568 cement Substances 0.000 description 11
- 241000196324 Embryophyta Species 0.000 description 9
- 239000000047 product Substances 0.000 description 9
- 230000001877 deodorizing effect Effects 0.000 description 7
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 6
- 244000005700 microbiome Species 0.000 description 6
- YYRMJZQKEFZXMX-UHFFFAOYSA-N calcium;phosphoric acid Chemical compound [Ca+2].OP(O)(O)=O.OP(O)(O)=O YYRMJZQKEFZXMX-UHFFFAOYSA-N 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 239000002426 superphosphate Substances 0.000 description 5
- 241000209094 Oryza Species 0.000 description 4
- 230000003213 activating effect Effects 0.000 description 4
- 210000003608 fece Anatomy 0.000 description 4
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 4
- 235000019796 monopotassium phosphate Nutrition 0.000 description 4
- PJNZPQUBCPKICU-UHFFFAOYSA-N phosphoric acid;potassium Chemical compound [K].OP(O)(O)=O PJNZPQUBCPKICU-UHFFFAOYSA-N 0.000 description 4
- 238000000746 purification Methods 0.000 description 4
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 3
- 241001465754 Metazoa Species 0.000 description 3
- 239000001569 carbon dioxide Substances 0.000 description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 description 3
- 238000010000 carbonizing Methods 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 230000029087 digestion Effects 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 239000011777 magnesium Substances 0.000 description 3
- 229910052749 magnesium Inorganic materials 0.000 description 3
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 description 3
- 239000000347 magnesium hydroxide Substances 0.000 description 3
- 229910001862 magnesium hydroxide Inorganic materials 0.000 description 3
- 230000007935 neutral effect Effects 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- 229910019142 PO4 Inorganic materials 0.000 description 2
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 description 2
- 230000009471 action Effects 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 229910052956 cinnabar Inorganic materials 0.000 description 2
- 230000001079 digestive effect Effects 0.000 description 2
- 230000012010 growth Effects 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 230000003472 neutralizing effect Effects 0.000 description 2
- 239000010452 phosphate Substances 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- 240000006108 Allium ampeloprasum Species 0.000 description 1
- 235000005254 Allium ampeloprasum Nutrition 0.000 description 1
- KRKNYBCHXYNGOX-UHFFFAOYSA-K Citrate Chemical compound [O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O KRKNYBCHXYNGOX-UHFFFAOYSA-K 0.000 description 1
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 125000000129 anionic group Chemical group 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 239000002374 bone meal Substances 0.000 description 1
- 229940036811 bone meal Drugs 0.000 description 1
- MYFXBBAEXORJNB-UHFFFAOYSA-N calcium cyanamide Chemical compound [Ca+2].[N-]=C=[N-] MYFXBBAEXORJNB-UHFFFAOYSA-N 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 235000012255 calcium oxide Nutrition 0.000 description 1
- ZOMBKNNSYQHRCA-UHFFFAOYSA-J calcium sulfate hemihydrate Chemical compound O.[Ca+2].[Ca+2].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O ZOMBKNNSYQHRCA-UHFFFAOYSA-J 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 235000013877 carbamide Nutrition 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 239000007857 degradation product Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 230000003450 growing effect Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 230000036571 hydration Effects 0.000 description 1
- 238000006703 hydration reaction Methods 0.000 description 1
- 230000008595 infiltration Effects 0.000 description 1
- 238000001764 infiltration Methods 0.000 description 1
- ZLNQQNXFFQJAID-UHFFFAOYSA-L magnesium carbonate Chemical compound [Mg+2].[O-]C([O-])=O ZLNQQNXFFQJAID-UHFFFAOYSA-L 0.000 description 1
- 239000001095 magnesium carbonate Substances 0.000 description 1
- 229910000021 magnesium carbonate Inorganic materials 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 229920002401 polyacrylamide Polymers 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 239000001103 potassium chloride Substances 0.000 description 1
- 235000011164 potassium chloride Nutrition 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 230000000246 remedial effect Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000012258 stirred mixture Substances 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/78—Recycling of wood or furniture waste
Landscapes
- Fertilizers (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
Abstract
Description
本発明は、軟弱土や汚泥に強度を持たせるとともに、土壌本来の力である、消化能力、浄化能力、通気能力、還元能力を高める固化材に関する。 The present invention relates to a solidifying material that gives strength to soft soil and sludge and enhances digestion ability, purification ability, ventilation ability, and reduction ability, which are the inherent powers of soil.
軟弱土や汚泥の土壌地は、農作物成育条件が整わないので、農地として利用することができない。また、そのままでは土壌地に立ち入ることさえも容易でない。軟弱土や汚泥の土質改良には、固化材を用いる固化処理が施される。また、固化材は、軟弱土や汚泥の土質改良をするときだけではなく、土木工事に伴って発生する土、腐食土等を搬出するときなどにも使用される。この場合、土壌の固化処理を施した後、搬出を行う。これまで、セメント系及び石灰系固化材を用いた土壌の固化処理が実施されている。 Soft soil and sludge soil cannot be used as farmland because the conditions for growing crops are not met. Moreover, it is not easy to enter the soil as it is. To improve the soil quality of soft soil and sludge, a solidification process using a solidifying material is performed. Further, the solidifying material is used not only when improving the soil quality of soft soil and sludge, but also when carrying out soil, corroded soil, etc. generated by civil engineering work. In this case, after carrying out the solidification treatment of the soil, it is carried out. So far, solidification treatment of soil using cement-based and lime-based solidifying materials has been carried out.
セメント系及び石灰系固化材は、セメント、生石灰等の無機質の粉末からなり、水で練り、型に流しこんだり塗りこんだりして放置すると、水和作用により凝固・硬化する。セメント系及び石灰系固化材で固めることにより耐久性に富む構造物を形成することができる。しかし、セメント系固化材は、原料に必然的に六価クロム(Cr6+)を含有し、その流出が懸念されている。また、有機質土壌や高含水土壌を十分に固めることができない。また、セメント系及び石灰系固化材を使用して固化処理した土壌はpHが11〜14程度と強アルカリ性を示し、生物が付着繁殖しにくいため、生態系に悪影響を及ぼすとされている。さらに、この改良土壌に雨水や地下水等が浸透することにより生じる浸出水が周辺環境に悪影響、すなわちアルカリ公害を引き起こす虞があった。これを防止するために、酸性の化学物質を用いて中和する試みがなされているが、この場合には、改良土壌の固化強度が低下して、必要とする強度が得られない場合が生じていた。 Cement-based and lime-based solidified materials are composed of inorganic powders such as cement and quicklime, and are solidified and hardened by hydration when they are kneaded with water and poured into a mold or left to stand. A structure rich in durability can be formed by solidifying with cement-based and lime-based solidifying materials. However, cement-based solidified materials inevitably contain hexavalent chromium (Cr 6+ ) in the raw material, and there is concern about the outflow. Moreover, organic soil and high water content soil cannot be hardened enough. In addition, soil solidified using cement-based and lime-based solidified materials has a strong alkalinity with a pH of about 11 to 14, and organisms are less likely to adhere to and propagate. Furthermore, the leachate produced by the infiltration of rainwater, groundwater, etc. into the improved soil may cause adverse effects on the surrounding environment, that is, cause alkali pollution. In order to prevent this, attempts have been made to neutralize using acidic chemicals. In this case, however, the solidification strength of the improved soil is reduced, and the required strength may not be obtained. It was.
セメント系及び石灰系固化材以外の固化材として軽焼マグネシアを成分とする固化材が開発されている。特許文献1には、軽焼マグネシアを主成分とする土壌硬化組成物が開示されている。特許文献2には、軽焼マグネシアを含む土壌固化材が開示されている。また、特許文献3には、軽焼マグネシアを含む汚泥用固化処理材が開示されている。軽焼マグネシアを成分とする固化材は、セメント系及び石灰系固化材と同程度の強度の固化作用を有するだけでなく、セメント系及び石灰系固化材を用いた土壌に比べてpHを低くし、土壌のアルカリ性を解消した環境に負荷の少ないものとなっている。また、軽焼マグネシア固化物は粉砕して土壌と混合しても土壌環境に影響を与えず、肥料分として還元されるという利点がある。 Solidification materials containing light-burned magnesia as a component have been developed as solidification materials other than cement-based and lime-based solidification materials. Patent Document 1 discloses a soil hardening composition mainly composed of light-burned magnesia. Patent Document 2 discloses a soil-solidifying material containing light-burned magnesia. Patent Document 3 discloses a solidification material for sludge containing light-burned magnesia. The solidified material composed of light-burned magnesia not only has the same solidifying action as cement-based and lime-based solidified materials, but also lowers the pH compared to soil using cement-based and lime-based solidified materials. It has become a less burdensome environment that eliminates the alkalinity of the soil. Further, even if the lightly burned magnesia solidified product is pulverized and mixed with soil, it does not affect the soil environment and has the advantage that it is reduced as fertilizer.
一方、土壌は、植物生産の基盤としての機能を持っていると同時に、地球上の元素循環の主要な部分を担い、生物の生息環境を恒常的に保つ働きを持つ。土壌における元素循環の流れは以下に示される。1.土壌中の有効微生物群が、落ち葉、動物の糞尿等の土壌中の有機物を分解する。2.分解物は土壌に還元され、この結果、活力のある土壌となる。3.活力のある土壌は、消化能力、浄化能力、通気能力、還元能力をさらに発揮する。
上述したように、軽焼マグネシアを用いた固化材は、セメント系及び石灰系固化材と比較して長所を有するが、活力のある土壌とする及び環境を浄化する効果に関しては十分な効果が得られていない。このため、固化材として優れた効果を有し、かつ活力のある土壌とする及び環境を浄化する効果に優れた固化材が望まれている。 As described above, the solidified material using light-burned magnesia has advantages compared to cement-based and lime-based solidified materials, but a sufficient effect is obtained with respect to the effect of making the soil vigorous and purifying the environment. It is not done. For this reason, there is a demand for a solidifying material that has an excellent effect as a solidifying material, and has a vigorous soil and an effect of purifying the environment.
そこで、本発明は、軟弱土や汚泥に強度を持たせるとともに、土壌本来の力である、消化能力、浄化能力、通気能力、還元能力を高める固化材を提供することを目的とする。 Therefore, an object of the present invention is to provide a solidified material that gives strength to soft soil and sludge and enhances digestion ability, purification ability, ventilation ability, and reduction ability, which are the inherent powers of soil.
上記課題を鑑みて鋭意検討した結果、軽焼マグネシアを含む固化材に炭を加えることにより、軟弱土や汚泥に強度を持たせるとともに、土壌本来の力である、消化能力、浄化能力、通気能力、還元能力を高める固化材を得られることを見出し、本発明に想到した。 As a result of diligent examination in view of the above problems, by adding charcoal to the solidified material containing light-burned magnesia, soft soil and sludge are given strength, and the soil's natural powers are digestion capacity, purification capacity, ventilation capacity. The present inventors have found that a solidified material that enhances the reducing ability can be obtained, and have arrived at the present invention.
本発明の請求項1の固化材は、土壌を固化する固化材において、軽焼マグネシア、軽焼マグネシア以外の他の肥料、及び炭を含むことを特徴とする。 The solidified material according to claim 1 of the present invention is a solidified material that solidifies soil, and includes light burned magnesia, fertilizer other than light burned magnesia, and charcoal.
本発明の請求項2の固化材は、土壌を固化する固化材において、軽焼マグネシア、軽焼マグネシア以外の他の肥料、及びアルカリ中和剤を含む組成物100重量部に対して、0.5〜10重量部の炭を含むことを特徴とする。 The solidified material according to claim 2 of the present invention is a solidified material for solidifying soil, in which 0.1 part by weight of the composition containing light burned magnesia, other fertilizers other than light burned magnesia, and an alkali neutralizer. It contains 5 to 10 parts by weight of charcoal.
本発明の請求項3の固化材は、前記請求項1又は2記載の固化材で、前記炭は、産業廃棄物が炭化されたものを含むことを特徴とする。 A solidified material according to a third aspect of the present invention is the solidified material according to the first or second aspect, wherein the charcoal includes carbonized industrial waste.
本発明の請求項4の固化材は、前記請求項3記載の固化材で、前記産業廃棄物が、家畜の糞尿、籾殻、木材チップ、草木又は食品のいずれか1つ以上であることを特徴とする。 The solidified material according to claim 4 of the present invention is the solidified material according to claim 3, wherein the industrial waste is any one or more of livestock manure, rice husk, wood chips, vegetation or food. And
本発明の請求項5の固化材は、請求項1〜4のいずれか1項記載の固化材で、前記炭が粉炭であることを特徴とする。 The solidification material according to claim 5 of the present invention is the solidification material according to any one of claims 1 to 4, wherein the charcoal is pulverized coal.
本発明の請求項6の土壌固化物の製造方法は、前記請求項1〜5のいずれか1項記載の固化材を土壌に添加し、攪拌することを特徴とする。 The method for producing a soil solidified product according to claim 6 of the present invention is characterized in that the solidified material according to any one of claims 1 to 5 is added to the soil and stirred.
本発明の請求項7の土壌固化物は、前記請求項6記載の土壌固化物の製造方法により得られたことを特徴とする。 The soil solidified product according to claim 7 of the present invention is obtained by the method for producing a soil solidified product according to claim 6.
本発明の請求項8の固化材は、土壌を固化する固化材において、その構成成分に炭を含み、かつ肥料成分に富み、軟弱土壌を改良するとともに土壌に活力を与え、作物や緑化に適することを特徴とする。 The solidified material according to claim 8 of the present invention is a solidified material for solidifying soil, which includes charcoal as a constituent component and rich in fertilizer components, improves soft soil and gives vitality to the soil, and is suitable for crops and greening. It is characterized by that.
本発明の請求項1によれば、軽焼マグネシアは土壌中の水分と結合すると水酸化マグネシウムとなり、その後空気中の炭酸ガスと反応して土壌の強度を増大させ、セメント系及び石灰系固化材に比べてpHが低く環境負荷の少ない土壌固化物とする。また、炭の多数の孔内に微生物が繁殖することにより、土壌本来の能力を発揮し、木の実、落ち葉、動物の排泄物や死骸、その他腐敗物を分解し、土壌を活性化できる。このため、農作物等の植物の生産に適した土壌を提供する。また、活力のある土壌は、上記腐敗物からの腐敗臭等の不快臭を浄化する働きもあるため、人が生活しやすい環境を提供する。また、軽焼マグネシア自体もマグネシウム成分として肥料となるとともに、軽焼マグネシア以外の他の肥料を加えることにより、土壌を活性化する効果を高めることができる。さらに、炭には元来から、脱臭作用があるため、腐敗臭等の不快臭の浄化の効果を高めることができる。 According to claim 1 of the present invention, light-burned magnesia becomes magnesium hydroxide when combined with moisture in the soil, and then reacts with carbon dioxide in the air to increase the strength of the soil. The soil solidified product has a low pH and a low environmental impact. In addition, microorganisms propagate in many holes of charcoal, thereby demonstrating the natural ability of the soil, decomposing nuts, fallen leaves, animal excrement and carcasses, and other septics, and activating the soil. For this reason, the soil suitable for production of plants, such as farm products, is provided. In addition, vigorous soil also has a function of purifying unpleasant odors such as rot odors from the rots, thus providing an environment where people can easily live. Moreover, while lightly burned magnesia itself becomes a fertilizer as a magnesium component, the effect of activating the soil can be enhanced by adding other fertilizers other than lightly burned magnesia. Furthermore, since charcoal has a deodorizing action from the beginning, the effect of purifying unpleasant odors such as spoiled odors can be enhanced.
本発明の請求項2によれば、軽焼マグネシアは土壌中の水分と結合すると水酸化マグネシウムとなり、その後空気中の炭酸ガスと反応して土壌の強度を増大させ、セメント系及び石灰系固化材に比べてpHが低く環境負荷の少ない土壌固化物とする。また、炭の多数の孔内に微生物が繁殖することにより、土壌本来の能力を発揮し、木の実、落ち葉、動物の排泄物や死骸、その他腐敗物を分解し、土壌を活性化できる。このため、農作物等の植物の生産に適した土壌を提供する。また、活力のある土壌は、上記腐敗物からの腐敗臭等の不快臭を浄化する働きもあるため、人が生活しやすい環境を提供する。また、軽焼マグネシア自体もマグネシウム成分として肥料となるとともに、軽焼マグネシア以外の他の肥料を加えることにより、土壌を活性化する効果を高めることができる。加えて、アルカリ中和剤によって、固化材のアルカリ成分を中和し、土壌中の微生物を含む草木の植物にとって適切である中性の土壌環境を提供する。さらに、炭には元来から、脱臭作用があるため、腐敗臭等の不快臭の浄化の効果を高めることができる。 According to claim 2 of the present invention, light burned magnesia becomes magnesium hydroxide when combined with moisture in the soil, and then reacts with carbon dioxide in the air to increase the strength of the soil. The soil solidified product has a low pH and a low environmental impact. In addition, microorganisms propagate in many holes of charcoal, thereby demonstrating the natural ability of the soil, decomposing nuts, fallen leaves, animal excrement and carcasses, and other septics, and activating the soil. For this reason, the soil suitable for production of plants, such as farm products, is provided. In addition, vigorous soil also has a function of purifying unpleasant odors such as rot odors from the rots, thus providing an environment where people can easily live. Moreover, while lightly burned magnesia itself becomes a fertilizer as a magnesium component, the effect of activating the soil can be enhanced by adding other fertilizers other than lightly burned magnesia. In addition, the alkali neutralizing agent neutralizes the alkaline component of the solidified material and provides a neutral soil environment that is suitable for plant plants containing microorganisms in the soil. Furthermore, since charcoal has a deodorizing action from the beginning, the effect of purifying unpleasant odors such as spoiled odors can be enhanced.
本発明の請求項3によれば、産業廃棄物を炭化させ、その一部又は全部を本発明の炭として使用することにより、産業廃棄物を有効に処分できる。この産業廃棄物は土壌中で分解され浄化されると同時に、有機物として土壌中に還元され、土壌に活力を与える効果を有する。さらに、炭の脱臭作用により、産業廃棄物の不快臭を浄化する効果を有する。 According to claim 3 of the present invention, industrial waste can be effectively disposed of by carbonizing industrial waste and using part or all of it as charcoal of the present invention. This industrial waste is decomposed and purified in the soil, and at the same time, it is reduced into the soil as an organic substance and has an effect of giving vitality to the soil. Furthermore, it has the effect of purifying the unpleasant odor of industrial waste by the deodorizing action of charcoal.
本発明の請求項4によれば、家畜の糞尿、もみがら、炭、草木、食品といった産業廃棄物を炭化させ、その一部又は全部を本発明の炭として使用することにより、産業廃棄物を有効に処分できる。この産業廃棄物は土壌中で分解され浄化されると同時に、有機物として土壌中に還元され、土壌に活力を与える効果を有する。さらに、炭の脱臭作用により、産業廃棄物の不快臭を浄化する効果を有する。 According to claim 4 of the present invention, industrial waste such as livestock manure, rice husk, charcoal, vegetation, food is carbonized, and part or all of the industrial waste is used as the charcoal of the present invention. Can be disposed of effectively. This industrial waste is decomposed and purified in the soil, and at the same time, it is reduced into the soil as an organic substance and has an effect of giving vitality to the soil. Furthermore, it has the effect of purifying the unpleasant odor of industrial waste by the deodorizing action of charcoal.
本発明の請求項5によれば、炭を粉炭とすることにより、炭を固化材中に均等に分布させることができる。また、粉状だと物体の容積を取らないため、取り扱いやすくなる。 According to claim 5 of the present invention, charcoal can be evenly distributed in the solidified material by using charcoal as pulverized coal. Moreover, since it does not take up the volume of an object when it is powdery, it becomes easy to handle.
本発明の請求項6の土壌固化物の製造方法によれば、軟弱土や汚泥に強度を持たせるとともに、土壌本来の力である、消化能力、浄化能力、通気能力、還元能力を高める。このため、農作物の生産や土壌の緑化を促進できる。また、炭の脱臭作用より腐敗臭等の不快臭の浄化の効果を高めることができる。さらに、本製造方法で固化された土壌固化物は、目的に応じて搬出することができる。 According to the method for producing a solidified soil according to claim 6 of the present invention, soft soil or sludge is given strength, and digestive ability, purification ability, aeration ability, and reduction ability, which are the inherent powers of soil, are enhanced. For this reason, the production of crops and the greening of soil can be promoted. In addition, the effect of purifying unpleasant odors such as spoiled odors can be enhanced by the deodorizing action of charcoal. Furthermore, the solidified soil solidified by this production method can be carried out according to the purpose.
本発明の請求項7によれば、請求項6記載の製造方法で固化された土壌固化物を得ることができる。土壌固化物は目的に応じて搬出することができる。これらの搬出した土壌固化物は、道路路床盛土、構造物の裏込め、道路路体用盛土、道路法面及び道路の中央分離帯用土材、河川堤防土材等の土木工事用の土材、宅地・公園・緑地造成用の地盤改良土材、スポーツグランド用の土材、植生用の培土材、海浜の砂防林帯及び砂漠化防止帯等の用途に適宜好適に再利用することができる。また、川や湖沼等に堆積する底泥土を固化した土壌固化物を搬出することにより、水質の浄化ができる。さらに、土木工事に伴って発生する土、腐食土等を簡便に搬出することができる。 According to claim 7 of the present invention, a solidified soil solidified by the production method according to claim 6 can be obtained. The soil solidified product can be taken out according to the purpose. These exported soil solidified materials include road roadbed embankments, backfilling of structures, road road embankments, road slopes and road median strip materials, river bank embankment materials, etc. It can be reused appropriately and suitably for applications such as soil improvement soil for building land, parks and green spaces, soil for sports ground, cultivated soil for vegetation, beach sabo forest zone and desertification zone . Moreover, water quality can be purified by carrying out soil solidified material obtained by solidifying the bottom mud deposited in rivers and lakes. Furthermore, the soil, corroded soil, etc. generated with civil engineering work can be carried out easily.
本発明の請求項8によれば、その構成成分に炭を含み、かつ肥料成分に富み、軟弱土壌を改良するとともに土壌に活力を与えるので、農作物の生産や土壌の緑化に適する土壌を提供することができる。 According to claim 8 of the present invention, the component contains charcoal, is rich in fertilizer components, improves soft soil and gives vitality to the soil, and therefore provides soil suitable for crop production and soil greening. be able to.
以下、本発明の実施形態について詳細に説明する。 Hereinafter, embodiments of the present invention will be described in detail.
本発明は、土壌を固化する固化材において、軽焼マグネシア、軽焼マグネシア以外の他の肥料、及び炭を含むことを特徴とする固化材に関する。固化材には、軽焼マグネシア、軽焼マグネシア以外の他の肥料、及び炭以外にも任意の化学物質を含ませることができる。固化材を構成するものを均一に混合し、粉末状として、固化材にしてもよい。 The present invention relates to a solidified material for solidifying soil, comprising light-burned magnesia, fertilizer other than light-burned magnesia, and charcoal. The solidified material may contain any chemical substance other than light burned magnesia, fertilizer other than light burned magnesia, and charcoal. What constitutes the solidifying material may be uniformly mixed to form a solidified powder.
本発明の固化材は、軽焼マグネシア、軽焼マグネシア以外の他の肥料、及びアルカリ中和剤を含む組成物100重量部に対して、0.5〜10重量部の炭を含ませることができる。本発明において、軽焼マグネシア、軽焼マグネシア以外の他の肥料、アルカリ中和剤の重量比は、軽焼マグネシア:他の肥料:アルカリ中和剤=65〜85:2〜8:15〜25であり、より好ましい重量比は、軽焼マグネシア:他の肥料:アルカリ中和剤=75:5:20である。軽焼マグネシア、軽焼マグネシア以外の他の肥料、及びアルカリ中和剤を含む組成物100重量部に対して0.5〜10重量部の炭を含む固化材において、強力な土壌固化効果を得ることができる。炭が0.5重量部以下であると、炭の効果が弱く、炭が10重量部以上であると、土壌固化効果が弱くなり、土壌固化材として適していない。軽焼マグネシア、軽焼マグネシア以外の他の肥料、及びアルカリ中和剤を含む組成物100重量部に対して、約5重量部の炭を含んだ固化材が特に好ましい。 The solidified material of the present invention may contain 0.5 to 10 parts by weight of charcoal with respect to 100 parts by weight of the composition containing light burned magnesia, other fertilizers other than light burned magnesia, and an alkali neutralizer. it can. In the present invention, the weight ratio of light-burned magnesia, fertilizer other than light-burned magnesia, and alkali neutralizer is as follows: light-burned magnesia: other fertilizer: alkali neutralizer = 65-85: 2-8: 15-25 A more preferable weight ratio is light-burned magnesia: other fertilizer: alkali neutralizer = 75: 5: 20. Light solid magnesia, other fertilizers other than light calcined magnesia, and solidified material containing 0.5 to 10 parts by weight of charcoal with respect to 100 parts by weight of the composition containing an alkali neutralizer, obtain a strong soil solidification effect. be able to. When charcoal is 0.5 parts by weight or less, the effect of charcoal is weak, and when charcoal is 10 parts by weight or more, the soil solidification effect is weakened and is not suitable as a soil solidifying material. A solidified material containing about 5 parts by weight of charcoal is particularly preferable with respect to 100 parts by weight of the composition containing light burned magnesia, other fertilizers other than light burned magnesia, and an alkali neutralizer.
本発明に用いられる軽焼マグネシアは、炭酸マグネシウムを800℃前後で焼成することにより得られる。軽焼マグネシアは土壌中の水分と結合すると水酸化マグネシウムとなり、その後空気中の炭酸ガスと反応して土壌の強度を増大させ、セメント系及び石灰系固化材に比べてpHが低く環境負荷の少ない土壌固化物とする。また、マグネシウム成分は植物の生育にとって必要な必須要素であり、軽焼マグネシアは、肥料としての機能も有する。 The light-burned magnesia used in the present invention is obtained by baking magnesium carbonate at around 800 ° C. Lightly burned magnesia becomes magnesium hydroxide when combined with soil moisture, and then reacts with carbon dioxide in the air to increase the strength of the soil and has a lower pH and less environmental impact than cement-based and lime-based solidified materials. Soil solidified material. The magnesium component is an essential element necessary for plant growth, and light-burned magnesia also has a function as a fertilizer.
本発明に用いられる軽焼マグネシア以外の他の肥料は、従来から知られている肥料を用いる。例として、尿素、硫酸アンモニウム、石灰窒素などの窒素肥料、過リン酸石灰、溶成リン肥などのリン酸肥料、塩化カリウムなどのカリウム肥料、牛糞尿堆肥、油かす、魚かす、骨粉などの有機質肥料が挙げられる。 Conventionally known fertilizers are used as fertilizers other than light-burned magnesia used in the present invention. Examples include nitrogen fertilizers such as urea, ammonium sulfate and lime nitrogen, phosphate fertilizers such as superphosphate lime and dissolved phosphorus fertilizer, potassium fertilizers such as potassium chloride, cow manure compost, oil grounds, fish grounds, bone meal, etc. Fertilizer is mentioned.
本発明に用いられるアルカリ中和剤は、アルカリ性の固化材成分を中和できる物質であれば限定されない。アルカリ中和剤によって、アルカリ性である軽焼マグネシアを中和できる。また、アルカリ中和剤によって、アルカリ性の固化材成分を中和し、土壌中の微生物を含む草木の植物にとって適切である中性の土壌環境を提供することができる。アルカリ中和剤の例としては、シュウ酸塩、クエン酸塩、リン酸塩、硫酸塩などが挙げられる。 The alkali neutralizer used in the present invention is not limited as long as it is a substance that can neutralize the alkaline solidifying material component. The light neutralized magnesia that is alkaline can be neutralized by the alkali neutralizer. Moreover, an alkaline solidifying agent component can be neutralized with an alkali neutralizing agent to provide a neutral soil environment that is suitable for plant plants containing microorganisms in the soil. Examples of the alkali neutralizer include oxalate, citrate, phosphate, sulfate and the like.
本発明の炭は、木材等を炭化して作ったものをさすが、その製法は限定されない。例えば、黒炭は木材を400℃〜700℃の温度で炭化させ、熱をさましてから取り出すことにより製法される。一方、白炭は窯で焼きあげている途中で空気を入れて温度を約1000℃まで上げ、最後に窯から取り出して灰をかけ、さますことにより製法される。蒸気を用いた炭の製造方法としてもよい。また、本発明の炭は粉末の状態の粉炭として用いてもよい。さらに、これらの組み合わせであってもよい。なお、炭の効能としては、1.炭の孔内に微生物が生育できる環境を提供する、2.土壌に活力を与える、3.浄化作用を有する、4.脱臭能力がある、等が従来から知られている。 The charcoal of the present invention refers to a material made by carbonizing wood or the like, but its production method is not limited. For example, black charcoal is produced by carbonizing wood at a temperature of 400 ° C. to 700 ° C., removing heat and then removing it. On the other hand, white charcoal is produced by putting air in the middle of baking in a kiln, raising the temperature to about 1000 ° C., and finally taking it out from the kiln and applying ash. It is good also as a manufacturing method of charcoal using steam. Moreover, you may use the charcoal of this invention as pulverized coal in a powder state. Further, a combination of these may be used. The charcoal has the following effects: 1. Provide an environment where microorganisms can grow in the pores of charcoal; 2. Energize the soil 3. has a purifying action; It has been known that it has a deodorizing ability.
また、本発明の炭は、産業廃棄物が炭化されたものを含む。炭は、その一部又は全部を産業廃棄物が炭化されたものから構成することができる。産業廃棄物としては、家畜の糞尿、もみがら、炭、草木、又は食品等が挙げられる。ただし、重金属などの有害物を含んでいる産業廃棄物は土壌を汚染するため、本発明の固化材の炭としては好ましくない。 Moreover, the charcoal of this invention contains what carbonized industrial waste. The charcoal can be partly or wholly composed of carbonized industrial waste. Examples of industrial waste include livestock manure, rice husk, charcoal, vegetation, and food. However, industrial waste containing toxic substances such as heavy metals contaminates the soil and is not preferable as the charcoal of the solidifying material of the present invention.
本発明の土壌固化物の製造方法は、軽焼マグネシア、軽焼マグネシア以外の他の肥料、及びアルカリ中和剤を含む組成物100重量部に対して、0.5〜10重量部の炭を含む本発明の固化材を土壌に添加し、攪拌することからなる。軽焼マグネシア、軽焼マグネシア以外の他の肥料、及びアルカリ中和剤を含む組成物100重量部に対して0.5〜10重量部の炭を含む固化材において、強力な土壌固化効果を得ることができる。炭が0.5重量部以下であると、炭の効果が弱く、炭が10重量部以上であると、土壌固化効果が弱くなり、土壌固化材として適していない。軽焼マグネシア、軽焼マグネシア以外の他の肥料、及びアルカリ中和剤を含む組成物100重量部に対して、好ましくは3〜7重量部の炭、より好ましくは約5重量部の炭を含んだ固化材が特に好ましい。 The method for producing a solidified soil according to the present invention comprises 0.5 to 10 parts by weight of charcoal with respect to 100 parts by weight of a composition comprising light burned magnesia, other fertilizers other than light burned magnesia, and an alkali neutralizer. The solidifying material of the present invention is added to the soil and stirred. Light solid magnesia, other fertilizers other than light calcined magnesia, and solidified material containing 0.5 to 10 parts by weight of charcoal with respect to 100 parts by weight of the composition containing an alkali neutralizer, obtain a strong soil solidification effect. be able to. When charcoal is 0.5 parts by weight or less, the effect of charcoal is weak, and when charcoal is 10 parts by weight or more, the soil solidification effect is weakened and is not suitable as a soil solidifying material. Preferably, 3 to 7 parts by weight of charcoal, more preferably about 5 parts by weight of charcoal is included with respect to 100 parts by weight of the composition comprising lightly burned magnesia, fertilizer other than lightly burned magnesia, and alkali neutralizer. Solidified material is particularly preferred.
本発明の固化材の用途としては、棚田、土水路、ため池等の法面を補強することが挙げられるが、これらに限定されない。例えば、宅地、公園、遊歩道等の軟弱土や汚泥を固化するために用いてもよい。 Applications of the solidifying material of the present invention include, but are not limited to, reinforcing slopes such as terraced rice fields, soil channels, and ponds. For example, it may be used to solidify soft soil and sludge such as residential land, parks, and promenades.
また、本発明の土壌固化物の製造方法で製造された土壌固化物は、目的に応じて搬出することができる。例えば、固化材を用いて、土木工事に伴って発生する土、腐食土等を固化処理し、搬出を行ってもよい。これらの搬出した土壌固化物は、道路路床盛土、構造物の裏込め、道路路体用盛土、道路法面及び道路の中央分離帯用土材、河川堤防土材等の土木工事用の土材、宅地・公園・緑地造成用の地盤改良土材、スポーツグランド用の土材、植生用の培土材、海浜の砂防林帯及び砂漠化防止帯等の用途に適宜好適に再利用することができる。 Moreover, the soil solidified material manufactured with the manufacturing method of the soil solidified material of this invention can be carried out according to the objective. For example, using a solidifying material, soil generated by civil engineering work, corrosive soil, or the like may be solidified and then carried out. These exported soil solidified materials include road roadbed embankments, backfilling of structures, road road embankments, road slopes and road median strip materials, river bank embankment materials, etc. It can be reused appropriately and suitably for applications such as soil improvement soil for building land, parks and green spaces, soil for sports ground, cultivated soil for vegetation, beach sabo forest zone and desertification zone .
以下、本発明の実施例を挙げて本発明を詳細に説明するが、本発明は下記の例に限定されるものではない。 EXAMPLES Hereinafter, although an Example of this invention is given and this invention is demonstrated in detail, this invention is not limited to the following example.
軽焼マグネシアの43.9重量部、半水石膏の56.1重量部、焼成ダストの97.5重量部、硅砂の31.7重量部、高分子凝集剤のアニオン系ポリアクリルアミドの3.66重量部、過リン酸石灰の10重量部を配合させた粉末状混合物を、軽焼マグネシアを含む組成物Aとした。次に、軽焼マグネシアを含む組成物A100重量部当たり、炭の5重量部を配合し、固化材Aを得た。木材を蒸し焼きにし、粉末状にしたものを炭とした。 43.9 parts by weight of light calcined magnesia, 56.1 parts by weight of hemihydrate gypsum, 97.5 parts by weight of calcined dust, 31.7 parts by weight of dredged sand, 3.66 of anionic polyacrylamide as a polymer flocculant A powdery mixture in which 10 parts by weight of 10 parts by weight of lime superphosphate was blended was designated as Composition A containing light-burned magnesia. Next, 5 parts by weight of charcoal was blended per 100 parts by weight of Composition A containing light-burned magnesia to obtain solidified material A. Wood was steamed and powdered to make charcoal.
固化材A30重量部、関東ローム100重量部(含水比42%)、水50重量部をホバートミキサーで3分間攪拌して、土壌固化物を得た。1日間室内で静置したところ、土壌固化物はほぼ固化し、3日間室内で静置すると、完全に固化した。固化した土壌10gを100mlの純水に浸漬してpH測定を行うと約10であった。 30 parts by weight of solidified material A, 100 parts by weight of Kanto loam (water content 42%), and 50 parts by weight of water were stirred with a Hobart mixer for 3 minutes to obtain a solidified soil. When it was allowed to stand indoors for 1 day, the solidified soil was almost solidified, and when it was left indoors for 3 days, it was completely solidified. When 10 g of solidified soil was immersed in 100 ml of pure water and the pH was measured, it was about 10.
実施例1の軽焼マグネシアを含む組成物A100重量部に、アルカリ中和剤としてリン酸二水素カリウム27重量部、及び炭5重量部を配合し、粉末状混合物である固化材Bとした。 27 parts by weight of potassium dihydrogen phosphate and 5 parts by weight of charcoal as an alkali neutralizer were blended with 100 parts by weight of composition A containing light-burned magnesia of Example 1 to obtain solidified material B which is a powdery mixture.
次に、固化材B30重量部、関東ローム100重量部(含水比42%)、水50重量部をホバートミキサーで3分間攪拌して、土壌固化物を得た。1日間室内で静置したところ、土壌固化物はほぼ固化し、3日間室内で静置すると、完全に固化した。固化した土壌10gを100mlの純水に浸漬してpH測定を行うと約8であった。実施例1と比較して、pHが中性に近く、アルカリ中和剤リン酸二水素カリウムの効果が確かめられた。 Next, 30 parts by weight of solidifying material B, 100 parts by weight of Kanto loam (water content 42%), and 50 parts by weight of water were stirred for 3 minutes with a Hobart mixer to obtain a solidified soil. When it was allowed to stand indoors for 1 day, the solidified soil was almost solidified, and when it was left indoors for 3 days, it was completely solidified. When 10 g of solidified soil was immersed in 100 ml of pure water and pH was measured, it was about 8. Compared with Example 1, the pH was close to neutral, and the effect of the alkali neutralizer potassium dihydrogen phosphate was confirmed.
軽焼マグネシアの50重量部、硅砂の47重量部、及び過リン酸石灰の3重量部からなる組成物100重量部当たりに、炭の5重量部を配合し、粉末状混合物である固化材Cを得た。木材を蒸し焼きにし、粉末状にしたものを炭とした。 5 parts by weight of charcoal is blended with 100 parts by weight of a composition comprising 50 parts by weight of light-burned magnesia, 47 parts by weight of cinnabar and 3 parts by weight of lime superphosphate, and solidified material C, which is a powdery mixture Got. Wood was steamed and powdered to make charcoal.
得られた固化材C15重量部と水田土壌100重量部(含水比61%)を混合攪拌し、1日間静置し固化土壌物を得た。その後、固化土壌物を鉢に敷き観葉植物を植えて、その生育状況を観察した(試験区)。対照として、固化材Cを用いない水田土壌のみを敷いた鉢における観葉植物の生育状況も観察した(対照区)。その結果、対照区に比して試験区の植物は葉の緑が強くつやがあり、健全な植物に成長した。固化材Cの添加により、試験区の土壌の質が改善され、活力のある土壌に変化したためと考えられる。 15 parts by weight of the obtained solidified material C and 100 parts by weight of paddy soil (water content ratio 61%) were mixed and stirred, and allowed to stand for 1 day to obtain solidified soil. Then, the solidified soil material was spread in a pot, a houseplant was planted, and the growth state was observed (test area). As a control, the state of growth of foliage plants in pots laid only with paddy soil without using solidifying material C was also observed (control group). As a result, the plants in the test group had strong green leaves and were shiny compared to the control group, and grew into healthy plants. It is thought that the addition of the solidifying material C improved the soil quality in the test area and changed to vigorous soil.
軽焼マグネシアの50重量部、硅砂の47重量部、及び過リン酸石灰の3重量部からなる組成物100重量部当たりに、15重量部のアルカリ中和剤リン酸二水素カリウムの、及び5重量部の炭を配合し、固化材Dを得た。木材を蒸し焼きにし、粉末状にしたものを炭とした。 15 parts by weight of the alkali neutralizer potassium dihydrogen phosphate and 5 parts per 100 parts by weight of a composition comprising 50 parts by weight of light-burned magnesia, 47 parts by weight of cinnabar and 3 parts by weight of lime superphosphate The charcoal of a weight part was mix | blended and the solidification material D was obtained. Wood was steamed and powdered to make charcoal.
得られた固化材D20重量部と牛の糞尿が混ざっている畑土壌100重量部(含水比55%)を混合攪拌し、1日間静置し固化土壌物を得た。固化土壌物の強度は固かった。また、炭の脱臭作用により、糞尿の不快臭は抑えられた。 20 parts by weight of the obtained solidified material D and 100 parts by weight of field soil (water content ratio 55%) mixed with cow manure were mixed and stirred, and allowed to stand for 1 day to obtain solidified soil. The strength of the solidified soil material was hard. Moreover, the unpleasant odor of manure was suppressed by the deodorizing action of charcoal.
軽焼マグネシアの77重量部、アルカリ中和剤であるリン酸二水素カリウムの18重量部及び過リン酸石灰の5重量部からなる組成物100重量部当たりに、炭の5重量部を配合し固化材Eを得た。木材を蒸し焼きにし、粉末状にしたものを炭とした。固化材E15重量部を水田土壌100重量部(含水比61%)へ加え、攪拌した。攪拌混合物を他の場所へ搬出し放置したところ、18時間経過後ほぼ完全に固化した。その後、固化物を地面に敷き均し、転圧した。2日後、転圧した箇所は固くなった。このことから、土壌固化物は、例えば、スポーツグランド用の土材として好適に用いることができることがわかった。 5 parts by weight of charcoal is blended per 100 parts by weight of a composition comprising 77 parts by weight of light-burned magnesia, 18 parts by weight of potassium dihydrogen phosphate as an alkali neutralizer and 5 parts by weight of lime superphosphate. Solidified material E was obtained. Wood was steamed and powdered to make charcoal. 15 parts by weight of solidifying material E was added to 100 parts by weight of paddy soil (water content ratio 61%) and stirred. When the stirred mixture was carried out to other places and allowed to stand, it was almost completely solidified after 18 hours. Thereafter, the solidified material was spread on the ground and rolled. Two days later, the rolled portion became hard. From this, it was found that the soil solidified material can be suitably used as an earth material for a sports ground, for example.
実施例5の固化材Eを土壌に添加し、農作物ネギに対する効果を調べた。比較例としては、固化材Eを添加しない土壌を使用した。その結果、本発明の固化材Eを添加した土壌で成育したものは、添加しない土壌で成育したものに比べて約1.2〜1.4倍の大きさを有した。このことより、本発明の固化材を用いた土壌は、優れた植物育成効果を有することがわかった。
The solidification material E of Example 5 was added to the soil, and the effect on the crop leek was examined. As a comparative example, soil to which the solidifying material E was not added was used. As a result, what grew on the soil to which the solidifying material E of the present invention was added was about 1.2 to 1.4 times larger than that grown on the soil without addition. From this, it was found that the soil using the solidifying material of the present invention has an excellent plant growing effect.
Claims (8)
Solidifying material for solidifying soil, which contains charcoal as a constituent component and rich in fertilizer components, improves soft soil and gives vitality to soil, and is suitable for crop production and soil greening .
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| JP2010240567A (en) * | 2009-04-03 | 2010-10-28 | Katsuhiko Ota | Improvement treatment method of construction sludge |
| US7877929B2 (en) | 2007-08-04 | 2011-02-01 | Rezzorb, Llc | Method and apparatus for reducing fertilizer use in agricultural operations |
| JP2012041679A (en) * | 2010-08-12 | 2012-03-01 | Shinyoo:Kk | Composition of soil solidified material manufacture and soil paving method |
| CN102603428A (en) * | 2012-03-12 | 2012-07-25 | 吴庆定 | Soil/carbon composite particles and preparation method thereof |
| CN118452026A (en) * | 2024-04-25 | 2024-08-09 | 河南大学 | A granular soil based on Yellow River sediment, preparation method and application thereof |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| JP2003226562A (en) * | 2002-02-05 | 2003-08-12 | National Institute For Rural Engineering | Environmental improvement cement composition |
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| JP2003226562A (en) * | 2002-02-05 | 2003-08-12 | National Institute For Rural Engineering | Environmental improvement cement composition |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7877929B2 (en) | 2007-08-04 | 2011-02-01 | Rezzorb, Llc | Method and apparatus for reducing fertilizer use in agricultural operations |
| JP2010240567A (en) * | 2009-04-03 | 2010-10-28 | Katsuhiko Ota | Improvement treatment method of construction sludge |
| JP2012041679A (en) * | 2010-08-12 | 2012-03-01 | Shinyoo:Kk | Composition of soil solidified material manufacture and soil paving method |
| CN102603428A (en) * | 2012-03-12 | 2012-07-25 | 吴庆定 | Soil/carbon composite particles and preparation method thereof |
| CN118452026A (en) * | 2024-04-25 | 2024-08-09 | 河南大学 | A granular soil based on Yellow River sediment, preparation method and application thereof |
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