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KR101108721B1 - Soil composition for ecological restoration greening and greening method using the same - Google Patents

Soil composition for ecological restoration greening and greening method using the same Download PDF

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KR101108721B1
KR101108721B1 KR1020110067930A KR20110067930A KR101108721B1 KR 101108721 B1 KR101108721 B1 KR 101108721B1 KR 1020110067930 A KR1020110067930 A KR 1020110067930A KR 20110067930 A KR20110067930 A KR 20110067930A KR 101108721 B1 KR101108721 B1 KR 101108721B1
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최경영
최승운
정연택
김형인
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주식회사 에코탑
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Abstract

본 발명의 토양미생물 군락을 이용한 녹화공법은 시공지역에 가장 인접한 자연환경에서 생육하는 미생물의 안정된 군락을 그대로 증식하여 사용하기 때문에 식물의 초기 생육에 유리한 조건을 형성하여 주변 자연식생과 어울릴 수 있도록 복원하여 빠른 녹화를 통한 바람직한 생태복원을 유도할 수 있으며, 녹화용 토양조성물에는 코코피트, 톱밥, 제지화이바 등 미생물 생육에 적합한 먹이 공급을 할 수 있는 성분이 포함되어 있어, 혼합된 미생물 군락이 지속적으로 생육 및 증식될 수 있는 환경을 제공할 수 있다.The greening method using the soil microbial community of the present invention restores to form a favorable condition for the early growth of the plant to match with the natural vegetation of the plant because it is used to multiply a stable colony of microorganisms growing in the natural environment closest to the construction area. It is possible to induce desirable ecological restoration through rapid greening, and the soil composition for greening contains ingredients that can be supplied for microbial growth, such as coco peat, sawdust, paper fiber, and the mixed microbial community It can provide an environment that can grow and multiply.

Description

생태복원 녹화용 토양조성물 및 그를 이용한 녹화공법 {SOIL COMPOSITION FOR RESTORING ECOLOGICAL GROUNDCOVERS AND METHOD USING THE SAME} Soil composition for ecological restoration greening and greening method using same {SOIL COMPOSITION FOR RESTORING ECOLOGICAL GROUNDCOVERS AND METHOD USING THE SAME}

본 발명은 친환경적이면서 식생이 원활히 이루어질 수 있는 미생물을 이용한 생태복원 녹화용 토양조성물 및 그를 이용한 녹화공법에 관한 것으로, 더욱 상세하게는 시공대상지 주변의 자연환경에서 채취한 토양에 생육하는 토양미생물군락의 안정된 군락구조를 그대로 증식한 토양미생물군락을 녹화용 토양조성물에 혼합하여 시공하며, 녹화용 토양조성물 또한 안정된 토양미생물군락이 원활하게 증식할 수 있도록 조성하여 토양의 구조와 비옥도를 지속적으로 유지하고 개선해 나가도록 할 뿐만 아니라, 식물의 초기 생육에 유리한 조건을 형성하여 주변 자연식생과 어울릴 수 있도록 복원하여 빠른 녹화를 통한 바람직한 생태복원을 유도할 수 있는 녹화용 토양조성물 및 그를 이용한 생태복원녹화공법(EGR, Ecological Groundcovers Restoration)에 관한 것이다.
The present invention relates to a soil composition for ecological restoration greening using microorganisms that can be environmentally friendly and smooth vegetation, and to a greening method using the same, and more specifically, to a microorganism of soil microorganisms growing in soil collected in the natural environment around the construction site. Construct and mix soil microbial communities that have grown in stable colony structure to greening soil composition, and also make green soil composition to grow smoothly to maintain and improve soil structure and fertility. As well as to go out, to create a favorable condition for the early growth of the plant to restore to match with the natural vegetation surrounding the greening soil composition that can induce desirable ecological restoration through rapid greening and ecological restoration greening method using the same (EGR , Ecological Groundcovers Restoration .

일반적으로 하천, 해안 및 도로의 절개지 등은 급경사지역, 표토층이 없거나 얇은지역, 또는 표토가 있더라도 척박한 지역이어서 식물이 생육하기 곤란한 환경이다. 이러한 환경에서 인공적으로 양호한 생장 환경을 조성해주기 위해서 다양한 식생녹화 공법들이 이용되어지고 있다. Generally, incisions of rivers, coasts, and roads are steep areas, no topsoil or thin layers, or even areas with poor topsoil, which are difficult to grow plants. In this environment, various vegetation greening methods are used to create artificially good growth environment.

대부분의 식생녹화공법은 다량의 식생토를 대상 비탈면 등에 두껍게 피복하고 여기에 종자, 비료, 접착제, 보습제, 피복양생제 등의 녹화 조성물을 대상지역에 분무하여 붙이는 식생기반재 뿜어붙이기 공법이 이용되어지고 있으나, 기존 녹화공법이 인공토양에 단지 종자를 혼합하여 취부하는 방식이어서 지속적인 관리가 뒤따르지 않으면 식물의 식생이 시간이 지날수록 떨어지는 단점이 있다.Most vegetation greening methods use vegetation-based material spraying method that coats large amount of vegetation soil thickly on target slope and sprays greening composition such as seed, fertilizer, adhesive, moisturizer and coating curing agent to the target area. However, because the existing greening method is a method of attaching only the seed to the artificial soil and attaching it, there is a disadvantage that the vegetation of the plant falls over time unless continuous management is followed.

녹화공법의 적용은 대상 비탈면의 경사도, 토질, 암질, 주변 경관 등의 여러 요인에 따라 다양하게 적용되고 있으며 취부방법에 따라 건식 형태와 습식 형태로 크게 구분되어 진다. 종자의 높은 발아율 및 빠른 활착을 위하여 보습제 및 황토, 활성탄, 톱밥, 부엽토, 하수오니 등 혼합물의 재료 및 구성에 대한 개발이 빠르게 진행되어지고 있다.
The greening method is applied in various ways according to the slope, soil, rock quality, surrounding landscape, etc., and it is classified into dry type and wet type according to the installation method. For the high germination rate and fast sticking of seeds, the development of materials and composition of moisturizers and mixtures such as loess, activated carbon, sawdust, foliar soil, sewage sludge are proceeding rapidly.

본 발명의 목적은 식물의 발아 및 초기 생장에 필요한 요건을 충족시켜 식물의 생장률과 장기적 천이를 유도하는 녹화용 토양조성물 및 이를 이용한 녹화공법을 제공하는 것이다.      SUMMARY OF THE INVENTION An object of the present invention is to provide a soil composition for greening and a greening method using the same, which induces plant growth rate and long-term transition by satisfying the requirements for plant germination and initial growth.

본 발명의 다른 목적은 성토 및 절토 구역에서도 식물의 발아 및 뿌리 착생능력을 개선시킬 수 있는 녹화용 토양조성물 및 이를 이용한 녹화공법을 제공하는 것이다. It is another object of the present invention to provide a greening soil composition and a greening method using the same, which can improve the germination and root growth ability of plants in the fill and cut areas.

상기와 같은 문제점을 해결하기 위한 본 발명에 의하면 사면녹화 시공대상지의 표토 또는 주변 자연환경에서 채취한 표토를 이용하여 배양한 토양미생물 군락 배양물을 함유하는 녹화용 토양조성물을 이용한 생태복원녹화공법이 제공된다.According to the present invention for solving the above problems, the ecological restoration greening method using the soil composition for greening containing the soil microbial colony culture cultured using the topsoil of the slope greening construction site or the topsoil collected from the surrounding natural environment Is provided.

본 발명의 생태복원 녹화공법은 (1) 절개지 주변 또는 유사한 자연환경에서 표토를 채취하는 과정; (2) 상기 채취한 표토를 배양하여 토양미생물 군락 배양물을 제조하는 과정; (3) 상기 토양미생물 군락 배양물을 함유하는 녹화용 토양조성물을 제조하는 과정; 을 포함하는 녹화용 토양조성물을 이용한 생태복원 녹화공법을 제공한다.      Ecological restoration greening method of the present invention (1) the process of collecting the topsoil around the incision or similar natural environment; (2) culturing the collected topsoil to produce a soil microbial colony culture; (3) preparing a greening soil composition containing the soil microbial colony culture; It provides an ecological restoration greening method using a soil composition for greening.

본 발명의 토양미생물 군락 배양물은 시공대상지의 표토 또는 주변 자연환경에서 채취한 표토를 이용하여 증식시킨 것으로서, 특정한 일부 미생물만이 아닌 자연환경에서 안정적인 군락을 형성하여 상호 균형을 이뤄 생육하고 있는 미생물군락인 것을 특징으로 한다. Soil microbial colony culture of the present invention is grown by using the topsoil of the construction site or the topsoil collected from the surrounding natural environment, microorganisms that grow in balance by forming a stable colony in the natural environment as well as some specific microorganisms. It is characterized by being a colony.

바람직하게, 상기 토양미생물 군락 배양물은 절개지 주변 또는 유사한 자연환경에서의 표토를 채취하여 볏짚, 부숙겨, 옥수수건초 및 흑설탕으로 이루어진 군으로 볏집 10중량%, 부숙겨 40중량%, 옥수수건초 40중량%, 흑설탕 10중량%로 이루어진 혼합물과 1:1000(표토: 혼합물)의 중량비로 혼합하여 습도 50%, 온도 40℃의 환경을 유지시켜 토양 미생물을 5일 동안 1차 배양시키고, Preferably, the soil microbial colony culture is a group consisting of rice straw, boiled bran, corn hay and brown sugar by collecting the topsoil around the incision or similar natural environment, 10% by weight of crest collection, 40% by weight of bran, corn hay 40% %, Mixture of 10% by weight brown sugar and weight ratio of 1: 1000 (topsoil: mixture) Maintain the environment with a humidity of 50% and a temperature of 40 ℃ by primary culture of soil microorganisms for 5 days,

상기 1차 배양된 배양물을 볏짚, 부숙겨, 옥수수건초 및 흑설탕으로 이루어진 군으로 볏집 10중량%, 부숙겨 40중량%, 옥수수건초 40중량%, 흑설탕 10중량%로 이루어진 혼합물과 1:1000(1차배양물:혼합물)의 중량비로 혼합하여 습도 50%, 온도 40 ℃의 환경을 유지시켜 5일 동안 2차 배양시켜 형성되는 것을 특징으로 한다.The primary culture was composed of rice straw, boiled bran, corn hay and brown sugar in the group consisting of 10% by weight of the crest, 40% by weight of bran, 40% by weight of corn hay, 10% by weight of brown sugar and 1: 1000 ( Primary cultures: mixtures) by mixing in a weight ratio of 50%, maintaining the environment at a temperature of 40 ℃ characterized in that it is formed by secondary culture for 5 days.

미생물을 배양하기 위해 사용된 볏짚과 부숙겨의 풍부한 탄수화물과 옥수수건초에 함유된 섬유질, 당분 그리고 흙설탕의 당분은 미생물의 먹이공급원이 되기 때문에 미생물의 배양을 왕성하게 할 수 있다.The rich carbohydrates of rice straw and boiled bran used to cultivate microorganisms and the sugars of fiber, sugars and sugar sugars contained in corn hay can be a source of microorganisms, which can lead to cultivation of microorganisms.

본 발명에서 녹화용 토양조성물은 주변 자연환경의 토양에서 채취하여 증식한 안정된 토양미생물 군락이 지속적이며 안정되게 생육 및 증식할 수 있는 조건을 갖춘 녹화용 토양조성물인 것을 특징으로 한다.In the present invention, the soil composition for greening is characterized in that the soil composition for greening with a condition that can be grown and propagated in a stable soil microbial colony collected and grown in the soil of the surrounding natural environment continuously and stably.

바람직하게, 녹화용 토양조성물은 2차 배양된 토양미생물 군락 배양물 5 내지 10 중량%, 코코피트 15 내지 25 중량%; 톱밥, 토탄 또는 이들의 혼합물 5 내지 10 중량%; 피복 양생제로 제지화이바 10 내지 20 중량%; 화강토 또는 마사토 30 내지 40 중량%; 접착제 5 내지 10 중량%, 유기성퇴비 5 내지 10 중량%를 포함하는 것을 특징으로 한다. Preferably, the soil composition for greening is 5 to 10% by weight of the second cultured soil microbial colony culture, 15 to 25% by weight of cocoite; 5 to 10% by weight of sawdust, peat or mixtures thereof; 10-20% by weight of papermaking bar as a coating curing agent; 30-40% by weight of granite or masato; It comprises 5 to 10% by weight of the adhesive, 5 to 10% by weight of organic compost.

코코피트는 야자껍질의 섬유층을 제거하고 초씨앗이 들어있지 않고 보수성과 보비력이 우수하여 좋은 토양기반재가 되며 염분함량, PH , 수분율, 불순물 등 품질이 안정되어있어 토착미생물 서식에 도움을 준다. Cocopit removes the fiber layer of palm bark, contains no seed seeds, has excellent water retention and maintenance ability, and is a good soil base material. Its quality is stable such as salinity, pH, moisture content, and impurities, which helps indigenous microbial habitat.

톱밥은 토양에서 공극을 넓혀주고 공기 공급을 원활하게 하여 식물근계의 호흡증진 및 토양 내 적정 수분 유지하고 토양내 비료효과와 토착미생물 활동촉진을 도우며 토양 산성화 및 토사유실을 방지하는데 도움을 준다.Sawdust widens the voids in the soil and facilitates the air supply, which helps to increase the respiration of the plant root system, maintain proper moisture in the soil, promote fertilizer effects and indigenous microbial activity, and prevent soil acidification and soil loss.

피복 양생제로 사용되는 제지화이바는 비탈면에 접착성을 가지며 골고루 섞여 법면녹화재로서의 역할을 수행할 수 있게 한다.Paper fiber used as coating curing agent has adhesiveness on the inclined surface and is evenly mixed so that it can act as a cotton greening material.

또한 상기 녹화용 토양조성물을 성토 또는 절토 구역에 초본류 또는 목본류 종자를 하나 이상 포함하여 0.5 내지 15cm의 두께로 피복하는 것을 특징으로 한다.In addition, the soil composition for greening is characterized in that it covers the thickness of 0.5 to 15cm including at least one herbaceous or woody seed in the fill or cut zone.

비탈면 녹화는 설계당시의 토질조건 및 주변 여건이 달라지므로 비탈면 발생지역의 기후 및 식생 특성과 비탈면 주변의 생태조건에 대한 조사를 실시하고 녹화복원목표, 종자선정 및 선구종의 설정, 시공두께의 적정성을 검토하며 훼손지 주변 또는 이와 유사한 자연상태의 표토층 시료를 채취하여 두어야 한다.Due to the different soil conditions and surrounding conditions at the time of design, slope greening is carried out to investigate climate and vegetation characteristics of slope-prone areas and ecological conditions around slopes, and to establish greening restoration targets, seed selection and pioneering species, and appropriateness of construction thickness. Samples of topsoil in the vicinity of the damaged area or similar natural state should be taken.

이어서 녹화기반토양의 취부시공에 앞서 시공비탈면의 흔들리는 장애물, 잡석 등 부착을 방해하는 물질을 제거하되, 산지에 뿌리를 내리고 있는 재래의 식물은 녹화기반 토양의 부착을 방해하지 않도록 지상부만 자르고 정리한 다음 녹화용 토양 조성물을 취부하여 식재기반을 조성한다.
Subsequently, remove obstacles such as shaking obstacles and rubble on the construction slope before installing the greening-based soil, but the conventional plants, which are rooted in mountain areas, are cut and cleaned only to prevent the attachment of the greening-based soil. Next, the soil composition for greening is mounted to form a planting base.

본 발명의 토양미생물 군락을 이용한 녹화공법은 시공지역에 가장 인접한 자연환경에서 생육하는 미생물의 안정된 군락을 그대로 증식하여 사용하기 때문에 식물의 초기 생육에 유리한 조건을 형성하여 주변 자연식생과 어울릴 수 있도록 복원하여 빠른 녹화를 통한 바람직한 생태복원을 유도할 수 있다.       The greening method using the soil microbial community of the present invention restores to form a favorable condition for the early growth of the plant to match with the natural vegetation of the plant because it is used to multiply a stable colony of microorganisms growing in the natural environment closest to the construction area. This can lead to desirable ecological restoration through rapid greening.

또한 녹화용 토양조성물에는 코코피트, 톱밥, 제지화이바 등 미생물 생육에 적합한 안정된 토양기반을 제공해 줌으로서 혼합된 미생물 군락이 지속적으로 생육 및 증식될 수 있는 환경을 제공할 수 있다.
In addition, the soil composition for greening provides a stable soil base suitable for the growth of microorganisms such as coco peat, sawdust, and paper fiber, thereby providing an environment in which the mixed microbial community can be continuously grown and expanded.

도 1은 시공전 절개지 사면의 사진이다.
도 2는 본 발명 시공중인 사진이다.
도 3은 본 발명에 의해 시공된 절개지 사면 녹화지의 사진이다.
1 is a photograph of the incision slope before construction.
2 is a photograph of the present invention construction.
Figure 3 is a photograph of the cut paper slope green paper constructed by the present invention.

이하 본 발명의 구성을 실시 예를 통하여 상세히 설명하기로 한다. 다만, 본 발명의 권리범위는 하기 실시 예에 의하여 한정되는 것은 아니다.
Hereinafter will be described in detail with reference to the configuration of the present invention. However, the scope of the present invention is not limited by the following examples.

실시예Example

토양미생물 군락 배양물 제조Soil Microbial Community Culture Preparation

미생물이란 보통 육안으로 볼 수 없는 0.1mm이하인 미세한 생물로서 세균, 사상균, 방선균 등으로 분류되고 있으며 토양 중에는 수십만 종의 미생물이 서식하면서 식물생육에 영향을 주고 있다. 이중 900여종이 유효 미생물, 100여종이 유해 미생물로 분류되고 있다. 이들은 좋은 방향이든 나쁜방향이든 상호 영향을 끼치며 번식, 생존해 가면서 탄소, 질소, 각종 미네랄의 순환에 관여하며 고등식물의 뿌리에 많은 영향을 미치고 있다. Microorganisms are microscopic organisms that are usually less than 0.1mm invisible to the naked eye and are classified into bacteria, filamentous fungi and actinomycetes. Hundreds of thousands of microorganisms in the soil affect plant growth. Of these, about 900 are classified as effective microorganisms and about 100 as harmful microorganisms. They have a mutual influence on both good and bad directions and are involved in the circulation of carbon, nitrogen, and various minerals as they multiply and survive, and affect the roots of higher plants.

최근 작물의 생육촉진 및 병해방지를 위해 Bacillus속, Trichoderma속, VA균근류 등 특정한 유용미생물을 이용한 미생물제제가 개발되어 이용되어지고 있다. 하지만 이러한 특정 미생물만을 첨가한 미생물제제는 수십만종의 미생물이 상호작용에 의해 안정적인 군락을 이루고 있는 자연상태에 사용된다면 미생물들간의 균형이 깨져 생태계 전체에 악영향을 미치거나, 첨가된 미생물이 토양에 정착하지 못하고 사멸되는 결과가 나타날 수 있다. Recently, microbial agents using specific useful microorganisms, such as Bacillus , Trichoderma , and VA fungi, have been developed and used to promote crop growth and prevent diseases. However, if the microorganisms added with only these specific microorganisms are used in a natural state in which hundreds of thousands of microorganisms form a stable colony by interaction, the balance between the microorganisms may be detrimental and adversely affect the entire ecosystem, or the added microorganisms may settle in the soil. The result may be death rather than failure.

따라서 본 발명에서는 시공대상지 주변의 자연환경에서 채취한 토양에 생육하는 토양미생물군락의 안정된 군락구조를 그대로 증식한 토양미생물군락을 녹화용 토양조성물에 혼합하여 시공하며, 녹화용 토양조성물 또한 안정된 토양미생물군락이 원활하게 증식할 수 있도록 조성하여 토양의 구조와 비옥도를 지속적으로 유지하고 개선해 나가도록 할 뿐만 아니라, 식물의 초기 생육에 유리한 조건을 형성하여 주변 자연식생과 어울릴 수 있도록 복원하여 빠른 녹화를 통한 바람직한 생태복원을 유도할 수 있는 녹화용 토양조성물 및 그를 이용한 생태복원녹화공법을 발명하고자 하였다. Therefore, in the present invention, the soil microbial colonies, which have grown in a stable colony structure of the soil microbial colonies growing in the soil collected in the natural environment around the construction site, are mixed with the greening soil composition, and the greening soil composition is also stable soil microorganisms. By allowing the colonies to grow smoothly, they not only maintain and improve the structure and fertility of the soil, but also create favorable conditions for the early growth of plants and restore them to match the natural vegetation around them. In order to induce desirable ecological restoration, we tried to invent a greening soil composition and an ecological restoration greening method using the same.

본 발명의 효과를 입증하기 위하여 대표적인 산림토양(참나무류 군락)에서 토양 시료를 채취하여 A, B, C, D, E의 서로 다른 배합비율을 갖는 혼합물과 1:1000표토: 혼합물)의 중량비로 혼합하여 습도 50%, 온도 40℃의 환경을 유지시켜 토양 미생물을 5일 동안 1차 배양시키고, 상기 1차 배양된 배양물을 다시 각각의 배합비율의 혼합물과 1:1000(1차배양물:혼합물)의 중량비로 혼합하여 습도 50%, 온도 40℃의 환경을 유지시켜 5일 동안 2차 배양하였다. In order to demonstrate the effect of the present invention, soil samples were collected from representative forest soils (oak communities), and the weight ratio of mixtures having different mixing ratios of A, B, C, D, E and 1: 1000 topsoil: mixture). Maintaining the environment at a humidity of 50% and a temperature of 40 ° C. to primary culture of the soil microorganisms for 5 days, and the primary culture was again mixed with a mixture of the respective mixing ratios of 1: 1000 (primary culture: The mixture was mixed at a weight ratio of 50% and maintained at an environment of 50% humidity and second culture for 5 days.

미생물의 증식에 적합한 토양미생물군락 배양물 조성을 위해 탄질비(C/N)에 따른 배양물의 부산물을 검토하여 적합한 재료를 [표 1]과 같이 선정하였다. In order to form a soil microbial culture suitable for the growth of microorganisms, by-products of the culture according to carbon ratio (C / N) were examined to select suitable materials as shown in [Table 1].

Figure 112011052528435-pat00001
Figure 112011052528435-pat00001

<표1> 토양미생물군락 배양물 선정
<Table 1> Soil Microbial Culture Selection

토양미생물은 세포를 증식하고 에너지를 발생하는데 탄소화합물을 대사물질로 이용한다. 그러나 어떤 생물체도 탄소만으로는 증식하고 생육할 수 없다. 미생물은 아미노산, 효소, DNA와 같은 질소합유 세포성분을 합성하는데 질소가 필요하므로 미생물의 먹이원, 에너지원으로 탄소와 질소가 반드시 필요하다. 표 1에서 볼 수 있듯이 평균 삼림 A층의 C/N비 20에 가까운 부산물을 배양물로 선정하여 미생물이 반드시 필요로 하는 탄소와 질소의 충분한 공급으로 먹이원을 확보해 안정된 토양미생물군락 배양물을 조성할 수 있다. Soil microbes use carbon compounds as metabolites to multiply cells and generate energy. But no organism can multiply and grow on carbon alone. Since microorganisms need nitrogen to synthesize nitrogen-synthesizing cell components such as amino acids, enzymes, and DNA, carbon and nitrogen are necessary as a source and energy source of microorganisms. As shown in Table 1, by-products close to the C / N ratio of the average forest A layer of 20 were selected as cultures, and a stable soil microbial colony culture was obtained by securing a food source with sufficient supply of carbon and nitrogen required by microorganisms. You can make it.

이렇게 선정된 토양미생물군락 배양물을 2차배양 후 2일 간격으로 각각의 구성 배합물에 존재하는 미생물의 종류별 계수를 실시하였다.[표 2-3]
Soil microbial cultures thus selected were subjected to counting by type of microorganisms present in each of the constituent blends at intervals of 2 days after the secondary culture. [Table 2-3]

Figure 112011052528435-pat00002
Figure 112011052528435-pat00002

<표2> 토양미생물 배양시험을 위한 배합구성비
<Table 2> Mixture Composition for Soil Microbial Culture Test

Figure 112011052528435-pat00003
Figure 112011052528435-pat00003

<표3> 각각의 구성 배합물에 존재하는 미생물의 종류별 계수Table 3: Coefficients by Type of Microorganisms in Each Composition

일반적 실험군으로 사용되는 부숙겨와 흑설탕만을 이용한 A구성에서의 총 미생물수는 배양 6일 후 145×104 으로 나타나 B구성(240×105), C구성(183×105), D구성(175×105), E구성(507×106)에 비하여 낮게 나타났다. 또한 전체 미생물중 세균, 방선균, 곰팡이, 트리코데마의 비율을 조사한 결과, 배양하지 않은 산림토양(자연상태의 미생물 분포)에서의 비율과 비교하여 볼때 세균과 방선균의 비율이 낮게 나타났으며 곰팡이와 트리코데마의 비율이 상대적으로 높게 나타났다. The total number of microorganisms in A composition using only boiled bran and brown sugar used as a general experimental group was 145 × 10 4 after 6 days of cultivation, resulting in B composition (240 × 10 5 ), C composition (183 × 10 5 ), and D composition ( 175 × 10 5 ) and lower than the E configuration (507 × 10 6 ). In addition, the ratio of bacteria, actinomycetes, fungi, and tricotema among all microorganisms showed that the ratio of bacteria and actinomycetes was lower than that of uncultivated forest soils (natural microbial distribution). The proportion of derma was relatively high.

볏짚, 옥수수 건초만을 이용한 B구성의 총 미생물수는 A구성(145×104)에 비해 상대적으로 높게 나타났지만 C구성(183×105), D구성(175×105), E구성(507×106)에 비해서는 상대적으로 낮게 나타났다. 전체 미생물중 종류별 분포비율을 배양하지 않은 산림토양과 비교해 볼 때, B구성은 세균, 방선균, 곰팡이의 비율이 감소했으며 트리코데마의 비율은 증가했다. C구성과 D구성의 미생물 비율은 여전히 낮지만 A구성과 B구성에 비해 산림토양 미생물 분포도에 가까워 지는것을 확인했다. The total number of microorganisms in B composition using rice straw and corn hay was relatively higher than A composition (145 × 10 4 ), but C composition (183 × 10 5 ), D composition (175 × 10 5 ), and E composition (507 × 10 6 ) was relatively low. Compared to the forest soils, the proportions of B-types were reduced in bacteria, actinomycetes, and fungi, and the percentage of trichodems was increased. Although the microbial ratios of C and D are still low, they are closer to the distribution of forest soil microorganisms than A and B.

본 발명의 가장 적합한 구성비율인 E구성은 다른 구성과 비교하여 볼 때 총 미생물수가 증가 했으며, 배양하지 않은 산림토양의 미생물 분포비율과 유사하게 나타났다.E composition, the most suitable composition ratio of the present invention, compared with other components, the total number of microorganisms increased, and appeared similar to the microbial distribution ratio of uncultivated forest soil.

위 결과를 볼 때 부숙겨와 흑설탕을 이용한 배합비율은 자연상태에서의 미생물전체밀도와 유사한 계수를 나타냈지만, 증식배양을 목적으로 한 결과에는 미치지 못했으며 미생물 종류별 비율도 자연상태의 비율과 상이하게 나타나, 자연상태의 비율을 유지하고자 하는 목적에 부합되지 않았다. B구성과, C구성, D구성에서는 자연상태에서의 미생물 전체밀도보다 높게 나타났지만 미생물의 종류별 비율에서는 한두종의 비율이 높아지거나 낮게 나타나, 자연상태의 비율을 유지하고자 하는 목적에 부합되지 않았다. 볏짚, 부숙겨, 옥수수건초, 흑설탕이 적합한 비율로 배합된 E구성의 배합비에서는 전체미생물 밀도가 다른 배합비율 및 배양하지 않은 산림토양에 비교하여 상대적으로 높게 나타났으며, 종류별 미생물 비율 또한 배양하지 않은 산림토양과 유사하게 나타났다. 이러한 결과는 일반적으로 미생물배양에 쓰이는 부숙겨, 밀당(흑설탕)배양보다 볏짚, 부숙겨 옥수수건초, 흑설탕이 대체하여 미생물의 먹이공급원으로서의 역할뿐만 아니라 미생물증식에 적당한 ph, 수분, 산소공급 등의 역할을 수행하여 자연상태에서의 미생물군락의 분포비율을 유지하며 증식되었다고 볼 수 있다.
From the above results, the mixing ratio using boiled bran and brown sugar showed similar coefficients to the total density of microorganisms in the natural state, but the results were not for the purpose of growth culture. It did not serve the purpose of maintaining the ratio of natural state. B, C and D showed higher than the total density of microorganisms in the natural state, but the ratio of one or two species was higher or lower in the ratio of microorganisms, which did not meet the purpose of maintaining the natural state. In the proportion of E composition containing rice straw, ripe bran, corn hay, and brown sugar in a suitable ratio, the total microbial density was relatively higher than that of other blended and uncultivated forest soils. Similar to forest soils. These results indicate that rice straw, boiled corn hay, and brown sugar are replaced by boiled bran, wheat sugar (brown sugar) culture, which is generally used for microbial culture, and not only as a food source for microorganisms but also as a suitable ph, moisture, and oxygen supply for microbial growth. It can be seen that the proliferation while maintaining the distribution ratio of the microbial community in the natural state.

녹화용 토양조성물 제조Manufacture of soil composition for greening

본 발명의 녹화용 토양조성물은 2차 배양된 토양미생물 군락 배양물 5 내지 10 중량%, 코코피트 15 내지 25 중량%; 톱밥, 토탄 또는 이들의 혼합물 5 내지 10 중량%; 피복 양생제로 제지화이바 10 내지 20 중량%; 화강토 또는 마사토 30 내지 40 중량%; 접착제 5 내지 10 중량%, 유기성퇴비 5 내지 10 중량%를 포함하여 제조하였다. Soil composition for greening of the present invention is secondary cultured soil microbial colony culture 5 to 10% by weight, coco peat 15 to 25% by weight; 5 to 10% by weight of sawdust, peat or mixtures thereof; 10-20% by weight of papermaking bar as a coating curing agent; 30-40% by weight of granite or masato; 5 to 10% by weight of the adhesive, and 5 to 10% by weight of organic compost were prepared.

본 발명에 의한 녹화용 토양조성물의 효과를 알아보기 위하여 토양조성물의 성분을 달리하여 톨훼스큐(Tall fescue)종자와 혼합하여 비탈면 절토 토사지역에 각각100㎡ 씩 시험시공한 후 1㎡(1M*1M) 방형구를 설치하여 식물의 생육상태를 조사하였다.
In order to investigate the effect of the soil composition for greening according to the present invention, the soil composition was mixed with Toll fescue seeds and tested for 100㎡ each in slope cut soil area, and then 1㎡ (1M * 1M). ) A spherical sphere was installed to check the growth of plants.

Figure 112011052528435-pat00004
Figure 112011052528435-pat00004

<표4> 녹화용 토양조성물의 식물생육상태 효과 조사 결과
<Table 4> Effect of Plant Growth Status of Soil Compositions for Greening

타입별 구성요소Type Specific Components

A타입 : 코코피트 10 중량%, 톱밥 10 중량%, 제지화이바 20 중량%, 마사토 40 중량%, 접착제 10 중량%, 유기성퇴비 5 중량%, 종자 5 중량%Type A: 10% by weight of cocopit, 10% by weight of sawdust, 20% by weight of paper fiber, Masato 40%, adhesive 10% by weight, organic compost 5% by weight, seed 5% by weight

B타입 : 본 발명에 의한 미생물군락 배양물 5 중량%, 코코피트 15 중량%, 톱밥 10 중량%, 제지화이바 10 중량%, 마사토 40 중량%, 접착제 5 중량%, 유기성퇴비 10, 종자 5 중량%Type B: 5% by weight of the microbial colony culture according to the present invention, cocoite 15% by weight, sawdust 10% by weight, paper fiber 10% by weight, Masato 40% by weight, adhesive 5% by weight, organic compost 10, seed 5% by weight

C타입 : 본 발명에 의한 미생물군락 배양물 10 중량%, 코코피트 10 중량%, 톱밥 10 중량%, 제지화이바 10 중량%, 마사토 40 중량%, 접착제 5 중량%, 유기성퇴비 10 중량%, 종자 5 중량%
Type C: 10% by weight of the microbial colony culture, 10% by weight of cocoite, 10% by weight of sawdust, 10% by weight of paper fiber, Masato 40% by weight, adhesive 5% by weight, organic compost 10% by weight, seed 5 weight%

녹화용 토양조성물의 혼합비율을 3가지 타입으로 구분하여 미생물의 혼합유무(A, B)와 미생물군락 배양물의 배합비율(B, C)로 나누어 비탈면 절토 토사지역에 각각100㎡ 씩 시험시공한 후 1㎡(1M*1M) 방형구를 설치하여 식물의 생육상태를 조사하였다. 시공 후 1주 간격으로 근장 및 초장을 조사한 결과 미생물이 전혀 혼합되지 않은 A타입의 경우 근장, 초장이 모두 낮게 나왔으며, 본 발명의 미생물군락 배양물을 5 중량% 포함한 녹화용 토양조성물(B) 보다, 미생물군란 배양물을 10 중량% 포함한 녹화용 토양조성물(C)이 시공 후 1주 간격으로 근장 및 초장을 조사한 결과 근장, 초장이 모두 우수한 것으로 나타났다. 녹화용 토양 조성물은 의 결과를 비교하여 보았을 때, 본 발명에 의한 미생물군락 배양물을 C 실험구 의 혼합비율로 혼합하였을 경우가 A, C 실험구보다 식물생육에서 높은 결과를 나타났다.After dividing the mixing ratio of soil composition for greening into three types and dividing it into the mixing ratio of microorganisms (A, B) and the mixing ratio (B, C) of microbial colony cultures, they were tested for 100㎡ in slope cut soil area. 1㎡ (1M * 1M) spherical spheres were installed to examine the growth of plants. As a result of irradiating root length and grass height at intervals of 1 week after construction, both root length and grass length appeared in the case of A type without microorganisms being mixed at all, and the greening soil composition (B) containing 5 wt% of the microbial colony culture of the present invention. Rather, the soil composition for greening (C) containing 10% by weight of the microbial population was found to be excellent in both root and grass lengths when the root length and grass length were examined at intervals of one week after construction. When the soil composition for greening was compared, the microbial colony culture according to the present invention showed a higher result in plant growth than the experimental group A and C when the mixing ratio of the experimental group was mixed.

Claims (4)

생태복원 녹화공법에 있어서,
(1) 절개지 주변 자연환경에서 표토를 채취하는 과정;
(2) 상기 채취한 표토를 배양하여 토양미생물 군락 배양물을 제조하는 과정;
(3) 상기 토양미생물 군락 배양물을 함유하는 녹화용 토양조성물을 제조하는 과정;을 포함하며,
상기 토양미생물 군락 배양물은 절개지 주변 자연환경에서의 표토를 채취하여 볏짚, 부숙겨, 옥수수건초 및 흑설탕으로 이루어진 군으로 볏집 10중량%, 부숙겨 40중량%, 옥수수건초 40중량%, 흑설탕 10중량%로 이루어진 혼합물과 1:1000(표토: 혼합물)의 중량비로 혼합하여 습도 50%, 온도 40℃의 환경을 유지시켜 토양 미생물을 5일 동안 1차 배양시키고, 상기 1차 배양된 배양물을 다시 볏짚, 부숙겨, 옥수수건초 및 흑설탕으로 이루어진 군으로 볏집 10중량%, 부숙겨 40중량%, 옥수수건초 40중량%, 흑설탕 10중량%로 이루어진 혼합물과 1:1000(1차배양물:혼합물)의 중량비로 혼합하여 습도 50%, 온도 40 ℃의 환경을 유지시켜 5일 동안 2차 배양시켜 형성되고,
상기 녹화용 토양조성물은 상기 미생물군락 배양물 10 중량%, 코코피트 10 중량%, 톱밥 10 중량%, 제지화이바 10 중량%, 마사토 40 중량%, 접착제 5 중량%, 유기성퇴비 10 중량%, 종자 5 중량%를 포함하며, 이 녹화용 토양조성물을 성토 또는 절토 구역에 초본류 또는 목본류 종자를 하나 이상 포함하여 0.5 내지 15cm의 두께로 피복하는 것을 특징으로 하는 녹화용 토양조성물을 이용한 생태복원 녹화공법.
In ecological restoration greening method,
(1) harvesting topsoil from the natural environment around the incision;
(2) culturing the collected topsoil to produce a soil microbial colony culture;
(3) preparing a soil composition for greening containing the soil microbial colony culture;
The soil microbial colony culture is a group consisting of rice straw, boiled bran, corn hay and brown sugar by collecting the topsoil from the natural environment around the incision, 10% by weight of the crest collection, 40% by weight of corn bran, 40% by weight of corn hay, 10% brown sugar. Mixed with a weight ratio of 1: 1000 (topsoil: mixture) and a weight ratio of 1: 1000 (topsoil: mixture) to maintain an environment of 50% humidity and a temperature of 40 ℃ to primary culture of soil microorganisms for 5 days, the primary culture was again Rice straw, boiled bran, corn hay and brown sugar in a group consisting of 10% by weight of rice straw, 40% by weight of bran, 40% by weight of corn hay, 10% by weight of brown sugar and 1: 1000 (primary culture: mixture) After mixing by weight ratio to maintain an environment of humidity 50%, temperature 40 ℃ is formed by secondary culture for 5 days,
The soil composition for greening is 10% by weight of the microbial culture, 10% by weight of coco peat, 10% by weight of sawdust, 10% by weight of paper fiber, Masato 40% by weight, adhesive 5% by weight, organic compost 10% by weight, seed 5 Ecological restoration greening method using a soil composition for greening, comprising a weight percent, covering the greening soil composition with a thickness of 0.5 to 15cm including at least one herbaceous or woody seed in the fill or cut zone.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101790710B1 (en) * 2017-05-15 2017-11-20 (주)동림피엔디 The device of restorer for an incline
KR102205462B1 (en) 2020-02-28 2021-01-20 주식회사 일림 Revegetation method usinf eco-friendly reinforcing material

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020077571A (en) * 2001-04-02 2002-10-12 경기산업개발 주식회사 Green Producing soil(GP Soil) Application
KR100735688B1 (en) * 2007-03-28 2007-07-04 동원녹화산업 (주) Soil composition for incline planting
KR101045661B1 (en) * 2011-01-12 2011-06-30 주식회사 에코탑 Vegetation mat using PLA

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020077571A (en) * 2001-04-02 2002-10-12 경기산업개발 주식회사 Green Producing soil(GP Soil) Application
KR100735688B1 (en) * 2007-03-28 2007-07-04 동원녹화산업 (주) Soil composition for incline planting
KR101045661B1 (en) * 2011-01-12 2011-06-30 주식회사 에코탑 Vegetation mat using PLA

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101790710B1 (en) * 2017-05-15 2017-11-20 (주)동림피엔디 The device of restorer for an incline
KR102205462B1 (en) 2020-02-28 2021-01-20 주식회사 일림 Revegetation method usinf eco-friendly reinforcing material

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