KR101436611B1 - Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral - Google Patents

Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral Download PDF

Info

Publication number
KR101436611B1
KR101436611B1 KR1020120103312A KR20120103312A KR101436611B1 KR 101436611 B1 KR101436611 B1 KR 101436611B1 KR 1020120103312 A KR1020120103312 A KR 1020120103312A KR 20120103312 A KR20120103312 A KR 20120103312A KR 101436611 B1 KR101436611 B1 KR 101436611B1
Authority
KR
South Korea
Prior art keywords
soil
weight
salt
parts
improving
Prior art date
Application number
KR1020120103312A
Other languages
Korean (ko)
Other versions
KR20140036776A (en
Inventor
박준홍
이은정
Original Assignee
주식회사 해강바이오
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 주식회사 해강바이오 filed Critical 주식회사 해강바이오
Priority to KR1020120103312A priority Critical patent/KR101436611B1/en
Publication of KR20140036776A publication Critical patent/KR20140036776A/en
Application granted granted Critical
Publication of KR101436611B1 publication Critical patent/KR101436611B1/en

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/40Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/08Reclamation of contaminated soil chemically
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2101/00Agricultural use
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2103/00Civil engineering use

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Soil Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Abstract

본 발명은 다공성 소결광물(macroporus inorganic mineral), 펄라이트(perlite), 분상코코피트(pulverized cocopeat), 황산석고(gypsum), 액상아미노산(amino acid liquid) 및 옥살산(oxalic acid)을 유효성분으로 포함하는 염류집적토양 개선용 토양개량제, 이의 제조방법 및 상기 토양개량제를 이용한 염류집적토양을 개량하는 방법을 제공한다.The present invention relates to a process for the production of microparticles comprising macroporous inorganic mineral, perlite, pulverized cocopeat, gypsum, amino acid liquid and oxalic acid as active ingredients The present invention provides a soil amendment agent for improving salt-accumulated soil, a method for producing the same, and a method for improving the salt-accumulated soil using the soil amendment agent.

Description

다공성 소결광물을 이용한 토양 내 염류집적 개선을 위한 토양개량제{Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral}TECHNICAL FIELD [0001] The present invention relates to a soil improvement agent for improving the accumulation of salts in a soil using a porous sintered mineral,

본 발명은 다공성 소결광물(macroporus inorganic mineral), 펄라이트(perlite), 분상코코피트(pulverized cocopeat), 황산석고(gypsum), 액상아미노산(amino acid liquid) 및 옥살산(oxalic acid)을 유효성분으로 포함하는 염류집적토양 개선용 토양개량제, 이의 제조방법 및 상기 토양개량제를 이용한 염류집적토양을 개량하는 방법을 제공한다.The present invention relates to a process for the production of microparticles comprising macroporous inorganic mineral, perlite, pulverized cocopeat, gypsum, amino acid liquid and oxalic acid as active ingredients The present invention provides a soil amendment agent for improving salt-accumulated soil, a method for producing the same, and a method for improving the salt-accumulated soil using the soil amendment agent.

염류집적(鹽類集積)은 강우가 적고 증발량이 많은 건조·반건조 지대의 토양 상층에서 하층으로의 세탈작용이 적고, 증발에 의한 염류의 상승량이 많아 표층에 염류가 집적하는 현상이다.Salt accumulation is a phenomenon in which salinity is accumulated on the surface layer due to low amount of salinity due to evaporation and low amount of sediment from the upper layer to the lower layer of dry and semi-dry area with low rainfall and high amount of evaporation.

시설하우스에서 관비 재배시 집적되는 염류의 관리는 연작이 오래될수록 해결하기 어려운 연작 문제의 하나이다. 하우스재배는 노지재배에 비하여 시설 내에서 작물을 집약적으로 재배하고 화학비료와 가축분뇨 등 시비량이 많아 대부분의 양분이 토양에 남게 되어 염류가 집적되면서 토양조건이 가스 및 병해충 발생이 많아지게 된다. 또한 강우의 영향을 받을 수 없는 하우스조건에서는 지표에서 지하로 물의 이동이 미약하고 관수에 의해서 물이 작토층 중에서 상하로 이동하게 되어 토양에서 시비양분의 용탈이 적게 되고 토양 중에 남게 된다. 작토층에서 물이 상하로 움직임에 따라 이에 함유된 염류가 표토에 집적하여 염류장해 문제가 발생하게 된다. 시설재배지에서는 폐쇄된 환경에서 작물의 재배횟수가 많고 고농도 화학비료와 가축분퇴비를 과도하게 시용하기 때문에 연작장해가 발생한다.The management of salt accumulation during the cultivation of the cabbage in the facility house is one of the series problems that are difficult to solve as the series becomes longer. As for the house cultivation, the crops are grown intensively in the facility compared to the non - cultivation, and the chemical fertilizer and livestock manure are many, so that most of the nutrients are left in the soil and the salt accumulation occurs. In the house condition, which is not influenced by rainfall, the movement of water from the surface to the basement is weak, and the water moves up and down in the soil layer by the irrigation water, so that the leaching of fertilizer nutrients in the soil is decreased and remains in the soil. As the water moves up and down in the soil layer, the salts contained in the soil layer accumulate on the topsoil, causing problems of salt obstruction. In plantation cultivation areas, cropping is frequently occurred in a closed environment, and excessive use of high-concentration chemical fertilizer and composting of livestock complements cropping.

염류집적은 작물의 생육을 저해하고 수량감소와 품질을 저하시키는 원인이 된다. 염류농도 증가에 따라 크게 관여하는 성분으로서는 NO3 -, Cl-, 및 SO4 2 - 등을 들 수 있으며 이들 성분을 함유하는 물질을 다량 시용할 때는 염류장해를 유념해야 한다. 농가들은 양분을 더 흡수하기 위하여 시비량을 더욱 증가시키며 이로 인해 토양의 염류농도는 더욱 높아지는 악순환이 계속되고, 양분은 토양에 집적되어 환경에도 해로운 영향을 끼칠 수 있다.Salinity accumulation inhibits the growth of crops and causes loss of yield and quality. The major components involved in the increase in salt concentration are NO 3 - , Cl - , and SO 4 2 - . It is important to pay attention to salt damage when using a large amount of these substances. Farmers continue to increase their fertilization to further absorb nutrients, which in turn causes a vicious cycle in which soil salt concentrations become higher, and nutrients can accumulate in the soil and have a detrimental effect on the environment.

하우스 재배에서 염류집적은 숙명적이지만 비료형태와 시비량에 주의하면 염류집적 속도를 지연시킬 수 있다. 보통 염류제거는 토양의 염류농도를 낮추는 것을 말하는데 방법을 크게 나누어 물을 이용한 염류제거, 작물을 이용한 염류제거, 그리고 유기물 시용에 의한 염류제거 등이 있다.In house cultivation, salt accumulation is fateful, but attention to fertilizer type and fertilizer amount can delay salt accumulation rate. Usually, the salt removal is to lower the salt concentration of the soil. There are two main methods to remove salts: water removal using salts, salt removal using crops, and salt removal using organic materials.

물을 이용한 염류제거는 다량의 깨끗한 물이 확보되어야 하나 토양물리성 개선이 우선하지 않을 시 그 효과를 기대하기 어렵다. 제염작물에 의한 염류제거는 작물과 제거 시기가 제염효과에 영향을 미친다. 유기물 사용에 의한 염류제거는 탄질율에 따라 제거효율이 달라지며 경우에 따라 염류농도를 증가시키거나 토양을 산성화시키는 역할도 한다. 그리고 피복제거는 염류집적 토양을 자연강우에 노출시키면 염류농도가 크게 감소된다. 따라서 고온으로 작물재배가 어려운 여름에 피복물을 제거하여 토양 중 염류농도를 낮추는 방법이 있으나 작물을 재배하지 못하여 발생하는 경제적인 손실이 크기 때문에 바람직한 방법은 아니다. 이외 염류제거 방법은 환토, 심토의 반전, 객토 등의 방법을 통하여 염류농도를 감소시킬 수 있으나 효과를 증대시키기 위해서는 반드시 적절한 토양개량제 처리가 필요하다.It is difficult to expect the effect of removal of salt from water when a large amount of clean water is secured but the improvement of soil physical properties does not take priority. Removal of salt by the decontamination crop affects the decontamination effect of the crop and removal timing. Removal of salts by using organic matter changes the removal efficiency according to the carbonitride ratio, and in some cases, it increases the salt concentration or acidifies the soil. And the removal of the coatings causes the salt concentration to be greatly reduced when the salt - accumulated soil is exposed to natural rainfall. Therefore, there is a method of lowering the concentration of the salt in the soil by removing the coating in the summer in which it is difficult to cultivate the crop at a high temperature, but this is not a desirable method because of the large economic loss caused by not growing the crop. In addition, the salt removal method can reduce the salt concentration by the method of flounder, inversion of the subsoil, and the soil, but proper soil remediation agent treatment is necessary to increase the effect.

따라서 기존 염류제거 방식에 적용이 가능할 뿐만 아니라 다양한 경로로 토양에 집적된 염류를 효과적으로 저감하며 토양의 이화학특성을 개선하기 위한 염류제거용 토양개량제 개발이 필요하다. 따라서 효과적으로 토양으로부터 집적된 염류를 제거하고 제거된 염류가 모세관 상승 또는 재가용화 등에 의하여 토양의 염도를 높이는 것을 방지하기 위한 토양개량제가 필요하다.Therefore, it is necessary to develop a soil remediation agent for desalting to improve the physico - chemical characteristics of soils by effectively reducing the salts accumulated in the soil in various ways as well as applying the conventional salt removal method. Therefore, there is a need for a soil remediation agent for effectively removing accumulated salts from the soil and preventing the removed salts from raising the salinity of the soil by raising the capillary or reusing it.

한국공개특허 제2006-0008142호에는 토양내 염류집적 개선제의 제조방법이 개시되어 있으나, 본 발명의 다공성 소결광물을 이용한 염류집적토양 개선을 위한 토양개량제 조성물과는 상이하다.Korean Patent Laid-Open Publication No. 2006-0008142 discloses a method for producing a salt accumulation-improving agent in soil, but is different from a soil-improving agent composition for improving salt-accumulated soil using the porous sintered mineral of the present invention.

본 발명은 상기한 종래 문제점을 해결하기 위한 것으로, 본 발명의 목적은 염류집적토양 내 염류농도를 효과적으로 낮추기 위해, 다공성 소결광물(macroporus inorganic mineral), 펄라이트(perlite), 분상코코피트(pulverized cocopeat), 황산석고(gypsum), 액상아미노산(amino acid liquid) 및 옥살산(oxalic acid)을 이용하여 제조된 염류집적토양 개량을 위한 토양개량제를 제공하는 데 있다.It is an object of the present invention to solve the above-mentioned problems of the prior art, and it is an object of the present invention to provide a method for effectively reducing the concentration of salts in a salt-accumulated soil by using a macroporus inorganic mineral, perlite, pulverized cocopeat, , Gypsum gypsum, amino acid liquid and oxalic acid. The present invention also provides a soil conditioner for soil improvement.

상기 과제를 해결하기 위해, 본 발명은 다공성 소결광물(macroporus inorganic mineral), 펄라이트(perlite), 분상코코피트(pulverized cocopeat), 황산석고(gypsum), 액상아미노산(amino acid liquid) 및 옥살산(oxalic acid)을 유효성분으로 포함하는 염류집적토양 개선용 토양개량제를 제공한다.In order to solve the above-mentioned problems, the present invention relates to a method for producing a microporous sintered body comprising macroporous inorganic mineral, perlite, pulverized cocopeat, gypsum, amino acid liquid and oxalic acid ) As an active ingredient. The present invention also provides a soil conditioner for soil improvement.

또한, 본 발명은 상기 염류집적토양 개선용 토양개량제의 제조방법을 제공한다.The present invention also provides a method for producing the soil amendment agent for improving the salt-accumulated soil.

또한, 본 발명은 상기 염류집적토양 개선용 토양개량제를 염류집적토양에 처리하는 단계를 포함하는 염류집적토양을 개량하는 방법을 제공한다.In addition, the present invention provides a method for improving a salt-accumulated soil comprising treating the salt-improving soil for improving the salt-accumulated soil.

본 발명의 토양개량제는 표면공극을 가지고 있는 다공성 소결광물(macroporus inorganic mineral, MIM)인 산업부산물자원을 대체 활용하기 때문에 경제성이 높다. 다공성 소결광물은 입경 조절에 따라 토양 내 안정화된 대공극을 형성하여 선택적 수분이동 통로 역할을 하여 제염 효율을 극대화하며 한편 모세관상승에 의한 재염화를 방지하는 효과도 있다. 특히 아미노산과 기타 식물영양은 MIM 내 양분이 다 소모되더라도 MIM은 토양에 남아 토양물리성을 개선할 뿐만 아니라 토양통기성 향상 등의 개선 효과가 있다. The soil improvement agent of the present invention is economically advantageous because it substitutes industrial by-product resources which are porous sintered minerals (macroporus inorganic minerals (MIM)) having surface voids. The porous sintered mineral forms stabilized pores in the soil according to the particle size control, thereby maximizing the decontamination efficiency by acting as a selective moisture transfer path, and also preventing recolonization due to capillary rise. In particular, amino acids and other plant nutrients, even when nutrients are consumed in the MIM, remain in the soil, not only improving the soil physical properties but also improving the soil permeability.

또한, 황산석고(gypsum)과 아미노산(amino acid)이 담지된 다공성 소결광물은 동일 토양수분포텐셜에서 수리전도도를 증가시켜 토양 내 집적된 염류의 하향이동성을 증가시킨다. 그리고 입상의 토양개량제를 토양에 처리 시 불포화 토양 수분상태에서 확산형태로 서서히 용해되어 식물생육기간 동안 17가지의 아미노산과 미량요소를 공급하여 뿌리발근 촉진뿐만 아니라 지상부 생장 촉진 효과가 있다.In addition, porous sintered minerals bearing sulfate gypsum and amino acid increase the hydraulic conductivity in the same soil water potential and increase the downward mobility of the accumulated salts in the soil. When the granular soil conditioner is applied to the soil, it gradually dissolves in the form of water in the unsaturated soil moisture, and it supplies 17 amino acids and trace elements during the plant growth period to promote root growth as well as promoting root growth.

또한, 본 발명의 토양개량제는 유기물 과다 집적에 따른 염류집적 토양에 효과적으로 염류집적을 개선할 수 있다. 그리고 간척지나 토양산도가 높은 시설재배지의 경우도 토양산도를 낮추는 역할을 하며, 토양개량제 내의 아미노산은 토양으로부터 뿌리로 이동되는 질산태 질소함량을 증가시키는 역할을 한다.Also, the soil amendment agent of the present invention can effectively improve the salt accumulation on the salt-accumulated soil due to the over-concentration of organic matter. Also, in the case of farms with high reclaimed land or soil acidity, it also plays a role of lowering soil acidity, and amino acid in the soil conditioner plays a role to increase nitrate nitrogen content moving from the soil to the roots.

도 1은 염류집적토양의 깊이에 따른 염류분포 특성(a)과 염류집적토양에 본 발명의 토양개량제를 처리한 후 토양 깊이에 따른 염류분포 특성(b)을 비교한 것이다.FIG. 1 is a graph comparing the characteristics (a) of the salt distribution according to the depth of the salt-accumulated soil and the salt distribution characteristic (b) according to the soil depth after treating the soil conditioner of the present invention with the salt-accumulated soil.

본 발명의 목적을 달성하기 위하여, 본 발명은 다공성 소결광물(macroporus inorganic mineral), 펄라이트(perlite), 분상코코피트(pulverized cocopeat), 황산석고(gypsum), 액상아미노산(amino acid liquid) 및 옥살산(oxalic acid)을 유효성분으로 포함하는 염류집적토양 개선용 토양개량제를 제공한다.In order to accomplish the object of the present invention, the present invention provides a method for producing a porous sintered mineral, comprising the steps of: mixing a mixture of a macroporous inorganic mineral, perlite, pulverized cocopeat, gypsum, amino acid liquid and oxalic acid oxalic acid) as an active ingredient.

상기 다공성 소결광물(macroporus inorganic mineral, MIM)은 일정 범위의 입경으로 선별된 매립제에 집섬을 첨가한 후 회화로(온도 650℃)에서 약 20분 정도 소결한 0.5 mm보다 크나 3.36 mm보다 작은 체를 통과한 입경의 매립제로 가공하여 사용할 수 있다. 다공성 소결광물 표면에 존재하는 표면 공극을 수분과 양분 보유기능 증대 목적으로 활용하기 위하여, 선별된 MIM을 액상아미노산(amino acid liquid, AAL)에 담지하면 기능성 다공체로 전환되어 배수성 증대와 통기성 개선 기능을 가지게 된다. 상기 다공성 소결광물은 세척석탄바닥재(washed coal bottom ash, CBA)일 수 있으나, 이에 제한되지 않는다.The macroporous inorganic mineral (MIM) was prepared by adding a sieve to a selected filler with a particle size of a certain range and then sieving the mixture at a temperature of 650 ° C for about 20 minutes, And then processed into an embedding material having a particle size that has passed through. In order to utilize surface voids present on the surface of porous sintered minerals for the purpose of enhancing moisture and nutrient holding function, when selected MIM is loaded on amino acid liquid (AAL), it is converted into functional porous body, I have. The porous sintered mineral may be, but is not limited to, washed coal bottom ash (CBA).

상기 펄라이트(perlite)는 제조과정 중 폐기물로 처리되는 입경 0.5 mm 이하의 소재를 사용할 수 있는데, 토양개량제의 경량화 및 토양에 처리 시 대공극 형성비율을 높여 수분 이동을 용이하게 하여 배수성과 통기성을 증진시키고 시설하우스의 경우 보온성을 유지시키는 역할을 한다.The perlite can be used as a material having a particle diameter of 0.5 mm or less to be treated as waste during the manufacturing process. The weight of the soil improving agent and the ratio of the pore formation during soil treatment can be increased to facilitate water movement, thereby improving drainage and ventilation And maintain the warmth in the case of the facility house.

상기 분상코코피트(pulverized cocopeat)는 원료를 분쇄하여 2 mm 체를 통과한 것을 사용할 수 있다. 단위 중량당 표면적과 물질 용출능의 증대뿐만 아니라, 보수력, 통기성, 배수성을 증대시키고 신축성을 유지하는 역할을 한다.The pulverized cocopeat may be obtained by pulverizing a raw material and passing the pulverized cocopeat through a 2 mm sieve. It not only increases surface area and material elution capacity per unit weight, but also increases water holding capacity, breathability, drainage and maintains elasticity.

상기 황산석고(gypsum)는 건조 후 전체 중량비로 환산하여 처리하였다. 칼슘과 황산이온 공급능을 증대하는 역할을 한다.The gypsum sulfate was dried and then converted to a total weight ratio. It plays a role in increasing calcium and sulfate ion supply ability.

상기 액상아미노산(amino acid liquid)은 고형상태의 젤라틴 원료를 수용화하여 액상상태의 아미노산으로 전환하여 사용하였다. 상토에서 지효성 질소와 17종의 아미노산 공급원 역할을 한다.The amino acid liquid was used to convert a solid gelatin raw material into a liquid state amino acid. It plays a role of supply of persistent nitrogen and 17 kinds of amino acids in the soil.

유기산의 일종인 상기 옥살산(oxalic acid)은 분말 결정체로서 카복실기 2개를 가지고 있으며 수용화 시 강산의 유기산인 것을 특징으로 한다.The oxalic acid, which is a kind of organic acid, is a crystalline powder having two carboxyl groups and is an organic acid of strong acid upon hydrolysis.

본 발명의 염류집적토양 개선용 토양개량제는 바람직하게는 토양개량제 100 중량부 기준으로, 다공성 소결광물(macroporus inorganic mineral) 30~36 중량부, 펄라이트(perlite) 45~55 중량부, 분상코코피트(pulverized cocopeat) 15~19 중량부, 황산석고(gypsum) 1~3 중량부, 액상아미노산(amino acid liquid) 1~3 중량부 및 옥살산(oxalic acid) 0.05~0.15 중량부를 유효성분으로 포함할 수 있으며,Preferably, the soil amendment agent for improving the salt-accumulated soil of the present invention comprises 30 to 36 parts by weight of macroporus inorganic mineral, 45 to 55 parts by weight of perlite, 15 to 19 parts by weight of pulverized cocopeat, 1 to 3 parts by weight of gypsum sulfate, 1 to 3 parts by weight of an amino acid liquid and 0.05 to 0.15 parts by weight of oxalic acid as an active ingredient ,

더욱 바람직하게는 토양개량제 100 중량부 기준으로, 다공성 소결광물(macroporus inorganic mineral) 33 중량부, 펄라이트(perlite) 50 중량부, 분상코코피트(pulverized cocopeat) 17 중량부, 황산석고(gypsum) 2 중량부, 액상아미노산(amino acid liquid) 2 중량부 및 옥살산(oxalic acid) 0.1 중량부를 유효성분으로 포함할 수 있다.More preferably, 33 parts by weight of a porous sintered mineral (macroporus inorganic mineral), 50 parts by weight of perlite, 17 parts by weight of pulverized cocopeat, 2 parts by weight of gypsum gypsum , 2 parts by weight of an amino acid liquid and 0.1 parts by weight of oxalic acid as an active ingredient.

본 발명은 또한, The present invention also relates to

(a) 다공성 소결광물(macroporus inorganic mineral) 30~36 중량부와 펄라이트(perlite) 45~55 중량부를 혼합한 혼합물에 황산석고(gypsum) 1~3 중량부 및 분상코코피트(pulverized cocopeat) 15~19 중량부를 혼합한 혼합물을 600~700℃에서 10~30분 동안 소결하는 단계;(a) 30 to 36 parts by weight of a macroporus inorganic mineral and 45 to 55 parts by weight of perlite are mixed with 1 to 3 parts by weight of gypsum gypsum and 15 to 30 parts by weight of a pulverized cocopeat, 19 to 10 parts by weight of a binder resin; and sintering the mixture at 600 to 700 占 폚 for 10 to 30 minutes;

(b) 젤라틴 분말을 55~65℃에서 1~3시간 동안 25~35 rpm으로 교반하여 액상아미노산(amino acid liquid)을 제조하는 단계;(b) stirring the gelatin powder at 55 to 65 ° C for 1 to 3 hours at 25 to 35 rpm to prepare an amino acid liquid;

(c) 상기 (b)단계의 제조된 액상 아미노산 1~3 중량부 및 옥살산(oxalic acid) 0.05~0.15 중량부를 혼합하여 혼합물을 제조하는 단계; 및(c) 1 to 3 parts by weight of the prepared liquid amino acid in step (b) and 0.05 to 0.15 part by weight of oxalic acid to prepare a mixture; And

(d) 상기 (a)단계의 소결시킨 혼합물에 상기 (c)단계의 혼합물을 분무한 후, 180~220℃에서 건조하는 단계를 포함하는 염류집적토양 개선용 토양개량제의 제조방법을 제공한다.(d) spraying the mixture of step (c) onto the sintered mixture of step (a) and drying the mixture at 180 to 220 ° C.

본 발명의 염류집적토양 개선용 토양개량제의 제조방법은 바람직하게는The method for producing the soil improving agent for improving salt-accumulated soil of the present invention is preferably

(a) 다공성 소결광물(macroporus inorganic mineral) 33 중량부와 펄라이트(perlite) 50 중량부를 혼합한 혼합물에 황산석고(gypsum) 3중량부 및 분상코코피트(pulverized cocopeat) 17 중량부를 혼합한 혼합물을 650℃에서 20분 동안 소결하는 단계;(a) A mixture of 33 parts by weight of a macroporus inorganic mineral and 50 parts by weight of perlite was mixed with 3 parts by weight of gypsum gum and 17 parts by weight of pulverized cocopeat. Lt; 0 > C for 20 minutes;

(b) 젤라틴 분말을 60℃에서 2시간 동안 30 rpm으로 교반하여 액상아미노산(amino acid liquid)을 제조하는 단계;(b) stirring the gelatin powder at 60 rpm for 2 hours at 30 rpm to prepare an amino acid liquid;

(c) 상기 (b)단계의 제조된 액상 아미노산 2 중량부 및 옥살산(oxalic acid) 0.1 중량부를 혼합하여 혼합물을 제조하는 단계; 및(c) mixing 2 parts by weight of the prepared liquid amino acid in step (b) and 0.1 part by weight of oxalic acid to prepare a mixture; And

(d) 상기 (a)단계의 소결시킨 혼합물에 상기 (c)단계의 혼합물을 분무한 후, 200℃에서 건조하는 단계를 포함할 수 있다.(d) spraying the mixture of step (c) onto the sintered mixture of step (a) and drying at 200 ° C.

본 발명은 또한, 상기 염류집적토양 개선용 토양개량제를 염류집적토양에 처리하는 단계를 포함하는 염류집적토양을 개량하는 방법을 제공한다.The present invention also provides a method for improving a salt-accumulated soil comprising treating the salt-improving soil for improving the salt-accumulated soil.

본 발명의 염류집적토양을 개량하는 방법은 바람직하게는 상기 염류집적토양 개선용 토양개량제를 염류집적토양 면적 8~12a 당 4400~5200 kg 처리할 수 있으며, 더욱 바람직하게는 면적 10a 당 4800 kg 처리할 수 있다. 보다 상세하게는 면적이 10a이고 깊이 20 cm 및 용적밀도 1.2 g/cm3인 염류집적토양의 무게 약 240톤을 기준으로 하여 본 발명의 염류집적토양 개선용 토양개량제를 2% 처리하는 것이 바람직하다.
The method for improving the salt-accumulated soil of the present invention is preferably such that the soil improvement agent for improving the salt-accumulated soil can be treated at 4400 to 5200 kg per 8-12a of salt-accumulated soil area, more preferably 4800 kg can do. More specifically it is preferred that the area 10a and the depth of 20 cm and the processing on the basis of about 240 ton of bulk density 1.2 g / cm 3 of salt accumulation soil to the salt accumulation soil amendment for soil improvement of the present invention 2% .

이하, 본 발명을 실시예에 의해 상세히 설명한다. 단, 하기 실시예는 본 발명을 예시하는 것일 뿐, 본 발명의 내용이 하기 실시예에 한정되는 것은 아니다.
Hereinafter, the present invention will be described in detail by way of examples. However, the following examples are illustrative of the present invention, and the present invention is not limited to the following examples.

제조예Manufacturing example 1: 염류집적토양 개선용 토양개량제의 제조 1: Manufacture of soil conditioner for soil improvement

(a) 세척석탄바닥재(washed coal bottom ash, CBA) 33 kg과 펄라이트(perlite, P) 50 kg을 혼합한 혼합물에 황산석고(gypsum) 2 kg 및 분상코코피트(pulverized cocopeat, PC) 17 kg을 첨가하여 650℃의 회화로에서 약 20분 동안 소결과정을 거쳤다.(a) To a mixture of 33 kg of washed coal bottom ash (CBA) and 50 kg of perlite (P), 2 kg of sulfuric acid gypsum and 17 kg of pulverized cocopeat (PC) And sintered in a painting furnace at 650 ° C for about 20 minutes.

(b) 젤라틴 분말을 가열수조에 넣고 60℃에서 2시간 동안 30 rpm으로 교반하여, 젤라틴분말을 완전히 용해시켜 수용성 상태인 액상아미노산(amino acid liquid)으로 전환시켰다.(b) Gelatin powder was added to a heated water bath and stirred at 60 rpm for 2 hours at 30 rpm to completely dissolve the gelatin powder and convert it into a water-soluble amino acid liquid.

(c) 상기 (b)단계의 전환된 액상 아미노산 2 kg 및 옥살산(oxalic acid) 0.1 kg을 혼합하여 혼합물을 제조하였다.(c) 2 kg of the converted liquid amino acid of step (b) and 0.1 kg of oxalic acid were mixed to prepare a mixture.

(d) 상기 (a)단계의 소결시킨 혼합물에 상기 (c)단계의 혼합물을 분무하여 상기 (a)단계의 혼합물 표면공극에 흡착시킨 후, 200℃에서 건조하였다.(d) The mixture of step (c) is sprayed on the sintered mixture of step (a), adsorbed on the surface of the mixture of step (a), and dried at 200 ° C.

원료별 이화학 특성Physicochemical characteristics of raw materials 원료Raw material pH
(1:5)
pH
(1: 5)
EC
(dS m-1)
EC
(dS m -1 )
CEC
(cmol kg-1)
CEC
(cmol kg -1 )
BD
(g cm-3)
BD
(g cm -3 )
OMOM T-NT-N NO3-NNO 3 -N NH4-NNH 4 -N Av.P2O5 Av.P 2 O 5 Ex.Cations (cmolc L-1)Ex.Cations (cmol c L -1 )
(mg L-1)(mg L -1 ) CaCa KK MgMg NaNa (%)(%) NaNa MIMMIM 7.87.8 0.150.15 8.58.5 1.041.04 0.10.1 NDND NDND NDND NDND <0.1&Lt; 0.1 <0.1&Lt; 0.1 <0.1&Lt; 0.1 <0.1&Lt; 0.1 PP 7.67.6 0.0180.018 7.07.0 0.130.13 0.60.6 0.00.0 0.20.2 1.01.0 5.75.7 0.80.8 0.00.0 0.20.2 2.12.1 PCPC 6.486.48 0.50.5 31.4631.46 0.160.16 9191 1.811.81 0.40.4 2.82.8 33.133.1 7.37.3 10.710.7 8.48.4 8.98.9

EC(Electric conductivity, 전기전도도), CEC(Cation exchange capability, 양이온치환용량), BD(bulk density, 용적밀도), OM(organic matter, 유기물 함량), T-N(총 질소), NO3-N(질산성 질소), NH4-N(암모니아성 질소), Av.P2O5(평균 인산 함량), Ex.Cations(치환성 양이온), ND(검출되지 않음)
EC (electrical conductivity), CEC (cation exchange capacity), BD (bulk density), OM (organic matter), TN (total nitrogen), NO 3 -N NH 4 -N (ammonia nitrogen), Av.P 2 O 5 (average phosphoric acid content), Ex.Cations (substitutional cation), ND (undetected)

실시예Example 1:  One: 토양개량제Soil improvement agent 처리에 따른 염류집적토양의 이화학 특성 Physico-chemical properties of salt-accumulated soils by treatment

실험에 사용된 염류농도가 높은 염류집적토양의 이화학적 특성은 하기 표 2와 같다. 하기 표 2와 같은 이화학적 특성을 지니는 염류집적토양을 본 발명의 토양개량제를 처리한 후 토양 내 염류 분포를 염류집적 지표인 전기전도도로 분석하였다. 그 결과, 토양개량제 처리가 토양 상층의 전기전도도를 감소시킴으로써, 본 발명의 토양개량제가 염류집적토양 개량을 위한 개량제로 효과적으로 사용할 수 있음을 확인할 수 있었다(도 1).The physicochemical properties of the salt-accumulated soil with high salt concentration used in the experiment are shown in Table 2 below. After the soil amendment agent of the present invention was treated with the salt-accumulating soil having physicochemical characteristics as shown in Table 2, the distribution of the salt in the soil was analyzed by the electric conductivity, which is a salt accumulation index. As a result, it was confirmed that the soil amendment agent of the present invention can be effectively used as an amendment agent for the improvement of salt accumulation soil by reducing the electric conductivity of the upper soil layer (FIG. 1).

염류집적토양의 이화학 특성Physicochemical properties of saline soils
Soil

Soil
pH
(1:5)
pH
(1: 5)
EC
(dS m-1)
EC
(dS m -1 )
OM(g kg-1)OM (g kg -1 ) CEC
(cmolc kg-1)
CEC
(cmol c kg -1 )

ESP(%)

ESP (%)
Particle size distribution
(%)
Particle size distribution
(%)
ClayClay SiltSilt SandSand SurfaceSurface 7.77.7 33.933.9 1.51.5 7.117.11 45.145.1 6.16.1 56.156.1 37.837.8 SubsurfaceSubsurface 7.87.8 14.714.7 1.51.5 7.197.19 56.256.2 5.45.4 57.157.1 37.537.5

EC(Electric conductivity, 전기전도도), OM(organic matter, 유기물 함량), CEC(Cation exchange capability, 양이온치환용량)EC (Electric conductivity), OM (organic matter), CEC (cation exchange capacity)

치환성 나트륨 백분율(Exchangeable sodium percentage, ESP) = Exchangeable Na+(cmolc kg-1)/CEC(cmolc kg-1) × 100Exchangeable sodium percentage (ESP) = Exchangeable Na + (cmol c kg -1 ) / CEC (cmol c kg -1 ) × 100

Claims (5)

토양개량제 100 중량부 기준으로, 세척석탄바닥재(washed coal bottom ash) 30~36 중량부, 펄라이트(perlite) 45~55 중량부, 분상코코피트(pulverized cocopeat) 15~19 중량부, 황산석고(gypsum) 1~3 중량부, 액상아미노산(amino acid liquid) 1~3 중량부 및 옥살산(oxalic acid) 0.05~0.15 중량부를 유효성분으로 포함하는 염류집적토양 개선용 토양개량제.30 to 36 parts by weight of washed coal bottom ash, 45 to 55 parts by weight of perlite, 15 to 19 parts by weight of pulverized cocopeat, gypsum ), 1 to 3 parts by weight of a liquid amino acid and 0.05 to 0.15 parts by weight of oxalic acid as an active ingredient. 삭제delete 삭제delete (a) 세척석탄바닥재(washed coal bottom ash) 30~36 중량부와 펄라이트(perlite) 45~55 중량부를 혼합한 혼합물에 황산석고(gypsum) 1~3 중량부 및 분상코코피트(pulverized cocopeat) 15~19 중량부를 혼합한 혼합물을 600~700℃에서 10~30분 동안 소결하는 단계;
(b) 젤라틴 분말을 55~65℃에서 1~3시간 동안 25~35 rpm으로 교반하여 액상아미노산(amino acid liquid)을 제조하는 단계;
(c) 상기 (b)단계의 제조된 액상 아미노산 1~3 중량부 및 옥살산(oxalic acid) 0.05~0.15 중량부를 혼합하여 혼합물을 제조하는 단계; 및
(d) 상기 (a)단계의 소결시킨 혼합물에 상기 (c)단계의 혼합물을 분무한 후, 180~220℃에서 건조하는 단계를 포함하는 염류집적토양 개선용 토양개량제의 제조방법.
(a) 30 to 36 parts by weight of washed coal bottom ash and 45 to 55 parts by weight of perlite are mixed with 1 to 3 parts by weight of gypsum gypsum and 15 parts by weight of pulverized cocopeat 15 To 19 parts by weight of a mixture is sintered at 600 to 700 ° C for 10 to 30 minutes;
(b) stirring the gelatin powder at 55 to 65 ° C for 1 to 3 hours at 25 to 35 rpm to prepare an amino acid liquid;
(c) 1 to 3 parts by weight of the prepared liquid amino acid in step (b) and 0.05 to 0.15 part by weight of oxalic acid to prepare a mixture; And
(d) spraying the mixture of step (c) onto the sintered mixture of step (a) and drying the mixture at 180 to 220 ° C.
제1항의 염류집적토양 개선용 토양개량제를 염류집적토양에 처리하는 단계를 포함하는 염류집적토양을 개량하는 방법.A method for improving a salt-accumulating soil, comprising treating the soil-improving soil for soil improvement of claim 1 with a salt-accumulating soil.
KR1020120103312A 2012-09-18 2012-09-18 Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral KR101436611B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR1020120103312A KR101436611B1 (en) 2012-09-18 2012-09-18 Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1020120103312A KR101436611B1 (en) 2012-09-18 2012-09-18 Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral

Publications (2)

Publication Number Publication Date
KR20140036776A KR20140036776A (en) 2014-03-26
KR101436611B1 true KR101436611B1 (en) 2014-09-02

Family

ID=50645951

Family Applications (1)

Application Number Title Priority Date Filing Date
KR1020120103312A KR101436611B1 (en) 2012-09-18 2012-09-18 Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral

Country Status (1)

Country Link
KR (1) KR101436611B1 (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010002046A (en) * 1999-06-10 2001-01-05 김재인 Method of soil reclamation pellet for rice crop of saline soil using gypsum and organics sludge
KR100955703B1 (en) 2009-09-28 2010-05-03 코스팜 주식회사 Eco-friendly soil conditioner composition containing aspartic acid-alkylaspartic acid copolymer for the decreased salt damage and taking root after plant transplanting and uses thereof
KR20110119318A (en) * 2010-04-27 2011-11-02 주식회사덕평그린 The composition for improving a soil and stimulating growth of a plant

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010002046A (en) * 1999-06-10 2001-01-05 김재인 Method of soil reclamation pellet for rice crop of saline soil using gypsum and organics sludge
KR100955703B1 (en) 2009-09-28 2010-05-03 코스팜 주식회사 Eco-friendly soil conditioner composition containing aspartic acid-alkylaspartic acid copolymer for the decreased salt damage and taking root after plant transplanting and uses thereof
KR20110119318A (en) * 2010-04-27 2011-11-02 주식회사덕평그린 The composition for improving a soil and stimulating growth of a plant

Also Published As

Publication number Publication date
KR20140036776A (en) 2014-03-26

Similar Documents

Publication Publication Date Title
CN107912098A (en) A kind of sand sticks the modification method of loamy texture saline-alkali soil
KR101805390B1 (en) Top soil composition for ecology restoration and method of ecology restoration using the same
CN103109615A (en) Improvement method for saline-alkali soil
Panova et al. Humics‐based interpolyelectrolyte complexes for antierosion protection of soil: Model investigation
CN110437844A (en) A kind of preparation of saline-alkali land soil conditioner and method of administration
CN111903467A (en) Process for improving marine silt for planting soil
KR101574608B1 (en) Revegetation method using eco-friendly soil composition for planting and stabilizing cut-slope
JP5010808B2 (en) Soil improvement method and soil improvement material
KR100955703B1 (en) Eco-friendly soil conditioner composition containing aspartic acid-alkylaspartic acid copolymer for the decreased salt damage and taking root after plant transplanting and uses thereof
Abo El-Ezz et al. Land Reclamation Using Compost, Agricultural Gypsum and Sugar Beet Mud.
Choudhary Use of amendments in ameliorating soil and water sodicity
CN110408405B (en) Acid soil conditioner, preparation method thereof and method for improving acid soil
KR101436611B1 (en) Soil conditioner for improving sodium accumulation in soil using macroporus inorganic mineral
CN103849405B (en) Lime dewatered sludge stabilizing agent and the using method thereof of heavy-metal composite pollution soil
KR101435184B1 (en) Greening soil and method for greening slope
KR101376192B1 (en) Bed soil for horticultural purpose using the illite and method of manufacturing the same
KR101652745B1 (en) Soil improvement material and preparing method thereof
CN110746239A (en) Mine soil restoration method and restoration material
KR101896779B1 (en) Bed soil composition for wild flower and its manufacturing method
Louhar Zeolites: A potential source of soil amendments to improve soil properties
KR101852125B1 (en) Soil Composition Containing Earthworm Casting for Developing Green Area, and Method for Manufacturing the Same
CN107739616A (en) Tea planting soil conditioner
KR101410250B1 (en) Bed soil for rice seeding for the growth control of microorganism and rhizosphere reinforcement and production method thereof
KR102582565B1 (en) The method of manufacturing soil improvement agents using stone and aggregate wastewater sludge and agricultural by-products
KR101301086B1 (en) Method of constructing ground for tree planting with dredged soil of reclaimed land from the sea

Legal Events

Date Code Title Description
A201 Request for examination
E902 Notification of reason for refusal
E701 Decision to grant or registration of patent right
FPAY Annual fee payment

Payment date: 20170619

Year of fee payment: 4

FPAY Annual fee payment

Payment date: 20180813

Year of fee payment: 5