KR102259169B1 - A method for manufacturing an environmentally friendly compost using waste sanitary articles and environmentally-friendly compost - Google Patents

A method for manufacturing an environmentally friendly compost using waste sanitary articles and environmentally-friendly compost Download PDF

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KR102259169B1
KR102259169B1 KR1020190084054A KR20190084054A KR102259169B1 KR 102259169 B1 KR102259169 B1 KR 102259169B1 KR 1020190084054 A KR1020190084054 A KR 1020190084054A KR 20190084054 A KR20190084054 A KR 20190084054A KR 102259169 B1 KR102259169 B1 KR 102259169B1
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compost
raw material
manufacturing
products
waste
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KR20210008239A (en
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전영철
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    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/50Treatments combining two or more different biological or biochemical treatments, e.g. anaerobic and aerobic treatment or vermicomposting and aerobic treatment
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F11/00Other organic fertilisers
    • C05F11/08Organic fertilisers containing added bacterial cultures, mycelia or the like
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

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  • General Chemical & Material Sciences (AREA)
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Abstract

본 발명은 펄프 재질의 습윤강력지 티슈 또는 기저귀 및 생리대 따위의 폐 위생용품을 이용하여 친환경 퇴비를 제조하는 방법에 관한 것으로, 준비된 폐 위생용품을 선별·세척·세절하여 주원료를 준비하는 전처리단계(S10); 준비된 주원료에 파쇄 처리된 산림부산물을 첨가하여 퇴비원료를 생성하는 혼합단계(S20); 생성된 퇴비원료에 미생물이 함유된 효소 액을 첨가하여 슬러지 상태로 조정하는 곤죽단계(S30); 슬러지로 조정된 퇴비원료를 32~38℃에서 1 내지 3일간 발효시켜 퇴비화 시키는 부숙단계(S40);를 포함하여 이루어지는 것을 특징으로 한다.
따라서 본 발명은 폐 위생용품을 재활용함으로써 원가의 절감으로 제조에 소요되는 전반적인 비용을 절감할 수 있을 뿐만 아니라 환경오염방지에 이바지할 수 있을 뿐만 아니라 탁월한 미생물로 인한 병원성 유해 곰팡이를 억제함으로써 고품질의 작물생장을 기대할 수 있는 효과가 있다.
The present invention relates to a method for manufacturing an eco-friendly compost by using a wet strong paper tissue made of pulp or waste hygiene products such as diapers and sanitary napkins, and a pre-treatment step of preparing the main raw material by selecting, washing, and washing the prepared waste hygiene products ( S10); A mixing step (S20) of generating a compost raw material by adding the crushed forest by-products to the prepared main raw material; Konjuk step (S30) of adjusting the sludge state by adding an enzyme solution containing microorganisms to the produced compost raw material; It is characterized in that it comprises a; composting step (S40) of fermenting the compost raw material adjusted to sludge at 32 ~ 38 ℃ for 1 to 3 days to compost.
Therefore, the present invention not only can reduce the overall cost of manufacturing by reducing costs by recycling waste hygiene products, but also contribute to the prevention of environmental pollution, and suppress pathogenic harmful fungi caused by excellent microorganisms to produce high-quality crops There is an effect that can be expected to grow.

Description

폐 위생용품을 이용한 친환경 퇴비의 제조방법 및 이에 제조된 친환경 퇴비{A method for manufacturing an environmentally friendly compost using waste sanitary articles and environmentally-friendly compost}A method for manufacturing an environmentally friendly compost using waste sanitary articles and environmentally-friendly compost

본 발명은 펄프 재질의 습윤강력지 티슈 또는 기저귀 및 생리대 따위의 폐 위생용품을 이용하여 친환경 퇴비를 제조하는 방법 및 이에 제조된 친환경 퇴비에 관한 것으로, 보다 구체적으로는 폐 위생용품을 재활용함으로써 제조에 소요되는 비용을 절감할 수 있음은 물론, 환경오염방지에 이바지할 수 있을 뿐만 아니라 친환경적이면서도 우수한 작물생장을 기대할 수 있는 폐 위생용품을 이용한 친환경 퇴비의 제조방법 및 이에 제조된 친환경 퇴비에 관한 것이다.The present invention relates to a method for manufacturing an eco-friendly compost using a pulp-made wet strong paper tissue or waste sanitary products such as diapers and sanitary napkins, and to the eco-friendly compost manufactured therefor, and more specifically, to the manufacturing by recycling waste sanitary products. It relates to a method for manufacturing an eco-friendly compost using waste sanitary products, which can reduce the cost, as well as contribute to the prevention of environmental pollution, and which can be expected to be eco-friendly and excellent crop growth, and to the eco-friendly compost manufactured therein.

오늘날 우리나라 유기성 폐기물의 급격한 증가와 이것의 소각 및 토양매립 처분으로 인한 환경오염이 사회적으로 심각한 문제로 대두되고 있다. 유기성 폐기물은 거의 대부분이 토양에서 미생물에 의해 분해될 수 있는 것으로 주방 폐기물, 농축산 폐기물, 도시하수 슬러지, 식료품 제조업 및 제지공장 등의 산업 폐기물이 이에 속한다.Today, the rapid increase of organic waste in Korea and environmental pollution caused by its incineration and landfill disposal is emerging as a serious social problem. Most organic wastes can be decomposed by microorganisms in the soil, and include kitchen waste, agricultural and livestock waste, municipal sewage sludge, and industrial waste such as food manufacturing and paper mills.

최근에는 병원이나 양로원, 가정 등에서 유아용 또는 성인용으로서 위생용품인 일회용 흡수물품의 사용이 증가하고 있다. 이러한 위생용품은 거의 전량 소각 처분되고 있는 실정인데, 사용된 위생용품은 시뇨 등의 수분을 포함하고 있으므로 연소 온도를 높게 하지 않으면 완전히 연소되지 않아 소각 처리비용의 증대 및 소각 시에 발생하는 이산화탄소의 배출량의 증가가 문제가 되고 있다.In recent years, the use of disposable absorbent articles as hygiene products for infants or adults in hospitals, nursing homes, and homes is increasing. Almost all of these sanitary products are incinerated. Since the sanitary products used contain moisture such as urine, they will not be completely burned unless the combustion temperature is raised, increasing the cost of incineration and the amount of carbon dioxide generated during incineration. increase is a problem.

이와 같은 문제를 해소하기 위한 일환으로 사용된 위생용품을 연료 등으로 이용하기 위한 여러 처리 방법이 제안되고 있는데, 예를 들어 고온 증기에 의한 탄화 처리법 및 식물성 기름 가열 가공 처리법 등을 들 수 있다.As a part of solving this problem, various treatment methods for using the used sanitary products as fuel, etc. have been proposed, for example, a carbonization treatment method using high-temperature steam and a heat processing method of vegetable oil.

하지만, 다량의 천연섬유를 포함하는 위생용품을 소각처리하거나 연료로 사용하는 것보다는 위생용품을 재 펄프화하거나 대한민국 등록특허공보 제10-0169065호와 대한민국 공개특허공보 제10-2001-0067661호에 개시된 것처럼 퇴비화 할 수 있는 방안이 필요하다.However, rather than incinerating or using a sanitary product containing a large amount of natural fiber as a fuel, re-pulp the sanitary product or Korean Patent No. 10-0169065 and Korean Patent Application Laid-Open No. 10-2001-0067661 As disclosed, a method capable of composting is needed.

그러나 통상의 폐지의 경우에는 물과 함께 교반하여 분해시킴으로써 재 펄프화가 가능하나, 특수 처리가 된 위생용품은 이러한 방법으로 분해시킬 수가 없다. 더구나 기존에 퇴비화 과정을 살펴보면, 최소 15일에서 최대 60일이 소요됨으로써 위생용품의 대량처리 내지 퇴비의 대량생산에 한계가 있다.However, in the case of normal waste paper, it is possible to re-pulp by disassembling it by stirring it with water, but sanitary products with special treatment cannot be decomposed in this way. Moreover, looking at the existing composting process, it takes at least 15 days to a maximum of 60 days, so there is a limit to mass processing of sanitary products or mass production of compost.

대한민국 등록특허공보 제10-0169065호 (발명의 명칭: 제지 슬러지의 비료화 공법)Republic of Korea Patent Publication No. 10-0169065 (Title of the invention: fertilization method of paper sludge) 대한민국 공개특허공보 제10-2001-0067661호 (발명의 명칭: 상업폐기물(제지 슬러지)과 황토를 이용한 유기성 퇴비조성물 제조 방법)Korean Patent Laid-Open Publication No. 10-2001-0067661 (Title of the invention: Manufacturing method of organic compost composition using commercial waste (paper sludge) and loess soil)

본 발명은 위의 제반 문제점을 보다 적극적으로 해소하기 위하여 창출된 것으로, 특수 처리된 위생용품을 저렴한 비용으로 분해시킴은 물론, 한 달에서 두 달 이상 소요되는 부숙기간을 현저히 단축하면서도 탁월한 미생물로 인한 병원성 유해 곰팡이를 억제함으로써 고품질의 작물생장을 기대할 수 있는 폐 위생용품을 이용한 친환경 퇴비의 제조방법 및 이에 제조된 친환경 퇴비를 제공하려는데 그 목적이 있다.The present invention was created to more actively solve the above problems, and it not only decomposes specially treated sanitary products at a low cost, but also significantly shortens the incubation period that takes from one to two months, while An object of the present invention is to provide a method for producing an eco-friendly compost using waste sanitary products that can expect high-quality crop growth by suppressing pathogenic harmful fungi and the eco-friendly compost manufactured therein.

위의 해결 과제를 달성하기 위하여 본 발명에서 제안하는 폐 위생용품을 이용한 친환경 퇴비의 제조방법 및 이에 제조된 친환경 퇴비의 구성은 다음과 같다.In order to achieve the above solution, the method for manufacturing an eco-friendly compost using waste sanitary products proposed in the present invention and the configuration of the eco-friendly compost manufactured therein are as follows.

위 폐 위생용품을 이용한 친환경 퇴비의 제조방법은 준비된 폐 위생용품을 선별·세척·세절하여 주원료를 준비하는 전처리단계; 준비된 주원료에 파쇄 처리된 산림부산물을 첨가하여 퇴비원료를 생성하는 혼합단계; 생성된 퇴비원료에 미생물이 함유된 효소 액을 첨가하여 슬러지 상태로 조정하는 곤죽단계; 슬러지로 조정된 퇴비원료를 32~38℃에서 1 내지 3일간 발효시켜 퇴비화 시키는 부숙단계;를 포함하여 이루어지는 것을 특징으로 한다.The manufacturing method of eco-friendly compost using the above waste sanitary products includes a pre-treatment step of preparing a main raw material by selecting, washing and shredding the prepared waste sanitary products; A mixing step of generating a compost raw material by adding the crushed forest by-products to the prepared main raw material; Konjuk step of adjusting the sludge state by adding an enzyme solution containing microorganisms to the produced compost raw material; It characterized in that it comprises; the composting step of fermenting the compost raw material adjusted to sludge at 32~38℃ for 1 to 3 days to make it compost.

이때, 본 발명에 의한 위 전처리단계는 준비된 폐 위생용품 중 불량 판정된 위생용품과 사용된 오염 위생용품을 분리한 다음, 분리된 오염 위생용품을 세척하여 이물질을 제거하면서 함유된 고 흡수성수지(Super Absorbent Polymer)의 물 흡수를 억제 처리한 이후, 불량 판정된 위생용품과 세척 처리된 위생용품을 1~5㎜ 크기로 세절하는 과정을 거치는 것을 특징으로 한다.At this time, the above pretreatment step according to the present invention separates the used contaminated hygiene products from the badly determined hygiene products among the prepared waste hygiene products, and then washes the separated contaminated hygiene products to remove foreign substances and contains super absorbent polymer (Super) Absorbent Polymer) is characterized in that it undergoes a process of slicing the sanitary products determined to be defective and the washed sanitary products into 1 to 5 mm size after treatment.

또한, 본 발명에 의한 위 전처리단계는 분리된 오염 위생용품을 물 70~90 중량%와 염화칼슘 30~10중량%가 혼합된 흡수억제제에 침지시켜 이물질을 제거하면서 함유된 고 흡수성수지의 물 흡수를 억제 처리하는 것을 특징으로 하는 폐 위생용품을 이용한 친환경 퇴비의 제조방법.In addition, in the above pretreatment step according to the present invention, the separated contaminated hygiene product is immersed in an absorption inhibitor mixed with 70 to 90% by weight of water and 30 to 10% by weight of calcium chloride to remove foreign substances and water absorption of the superabsorbent polymer contained therein. A method for producing an eco-friendly compost using waste sanitary products, characterized in that suppression treatment.

또한, 본 발명에 의한 위 혼합단계는 주원료 70~90 중량%에 열가소성수지 10~30 중량%를 혼합한 다음, 혼합물에 1~5㎜로 파쇄 처리된 나뭇가지와 톱밥 따위의 산림부산물을 1:1 중량비로 첨가한 이후 교반시켜 퇴비원료를 생성하는 것을 특징으로 한다.In addition, in the above mixing step according to the present invention, 10 to 30% by weight of a thermoplastic resin is mixed with 70 to 90% by weight of the main raw material, and then to the mixture, a forest by-product such as twigs and sawdust that is crushed to 1-5 mm is 1: It is characterized in that it is added in a weight ratio of 1 and stirred to produce a compost raw material.

또한, 본 발명에 의한 위 열가소성수지는 폴리염화비닐(poly vinyl chloride), 폴리스티렌(polystyrene), 폴리에틸렌(polyethylene), 폴리프로필렌(polypropylene), 아크릴(acrylic), 폴리아미드(polyamide)수지 중 어느 하나 또는 복합적으로 조성되는 것을 특징으로 한다.In addition, the above thermoplastic resin according to the present invention is any one of polyvinyl chloride, polystyrene, polyethylene, polypropylene, acrylic, polyamide resin or It is characterized by a complex composition.

또한, 본 발명에 의한 위 곤죽단계는 10% 염도를 가진 물 25L에 접종된 미생물이 37℃에서 3~5일간 배양된 효소 액을 첨가하여 pH 6.5~7.5 수분함수율 65~70%의 슬러지 상태로 조정하는 것을 특징으로 한다.In addition, in the stomach porridge step according to the present invention, the microorganism inoculated in 25L of water with 10% salinity is added to the enzyme solution cultured at 37 ° C. for 3 to 5 days to form sludge with a water content of 65 to 70% at pH 6.5 to 7.5. characterized by adjustment.

또한, 본 발명에 의한 위 미생물은 바실러스 리케니포르미스균 (Bacillus licheniformis), 바실러스 서브틸리스균 (Bacillus subtilis), 바실러스 스테아로스모필러스균 (Bacillus stearothermophillus) 중 어느 하나 또는 둘 이상 복합적으로 조성된 것을 특징으로 한다.In addition, the gastric microorganism according to the present invention Bacillus licheniformis (Bacillus licheniformis), Bacillus subtilis (Bacillus subtilis), Bacillus stearothermophillus (Bacillus stearothermophillus) any one or two or more of a composite composition characterized.

또한, 본 발명에 의한 위 효소 액은 미생물 배양된 물 25 중량%에 당밀 25 중량%, 비트펄프 20 중량%, 제올라이트 30 중량%가 첨가되는 것을 특징으로 한다.In addition, the gastric enzyme solution according to the present invention is characterized in that 25% by weight of molasses, 20% by weight of beet pulp, and 30% by weight of zeolite are added to 25% by weight of microbial cultured water.

또한, 본 발명에 의한 위 숙성단계는 슬러지로 조정된 퇴비원료를 밀폐된 교반기에 투입하여 35℃의 열풍을 1~2시간마다 1~2분 동안 공급하면서 24시간마다 3~6회 텀블링시키는 것을 특징으로 한다.In addition, in the above aging step according to the present invention, the compost raw material adjusted to sludge is put into a sealed agitator and tumbled 3 to 6 times every 24 hours while supplying hot air at 35° C. for 1 to 2 minutes every 1 to 2 hours. characterized.

본 발명에 의한 방법으로 제조된 퇴비는 수분함수율 40~50%를 지니고, 그램(g)당 바실러스 속(Bacillus spp) 1.4×107, 유산균(Lactic acid bacteria) 1.4×107로 함유된 것을 특징으로 한다.The compost produced by the method according to the present invention has a moisture content of 40-50%, and contains 1.4×10 7 Bacillus spp and 1.4×10 7 Lactic acid bacteria per gram (g). do it with

상술한 구성으로 이루어지는 본 발명에 의하면, 다음과 같은 효과를 제공한다.According to the present invention having the above-described configuration, the following effects are provided.

첫째, 폐 위생용품을 재활용함으로써 원가의 절감으로 제조에 소요되는 전반적인 비용을 절감할 수 있을 뿐만 아니라 환경오염방지에 이바지할 수 있다.First, by recycling waste sanitary products, it is possible not only to reduce the overall cost of manufacturing by reducing costs, but also to contribute to the prevention of environmental pollution.

둘째, 위생용품에 함유된 고 흡수성수지 기능을 보다 저렴한 비용으로 제작된 흡수억제제를 통해 억제 처리함으로써 퇴비의 가격경쟁력을 도모할 수 있다.Second, the price competitiveness of compost can be promoted by suppressing the function of the super absorbent polymer contained in sanitary products through an absorption inhibitor manufactured at a lower cost.

셋째, 한 달에서 두 달 이상 소요되는 부숙기간을 현저히 단축하면서도 위생용품의 속성 대량처리와 함께 퇴비의 속성 대량생산이 가능하다.Third, while remarkably shortening the fermenting period, which takes one to two months, it is possible to mass-produce compost along with rapid mass processing of sanitary products.

넷째, 부숙조건과 효소 액으로 우수한 퇴비화로 인해 미생물로 병원성 유해 곰팡이를 억제함으로써 고품질의 작물생장을 기대할 수 있다.Fourth, high-quality crop growth can be expected by suppressing pathogenic and harmful mold with microorganisms due to excellent composting conditions and enzyme solution.

도 1은 본 발명에 따른 제조과정을 전체적으로 간략하게 나타내는 순서도.
도 2는 본 발명에 따른 제조장치를 전체적으로 나타내는 사시도.
도 3은 본 발명에 따른 제조장치의 작동을 나타내는 제조상태도.
도 4 및 도 5는 본 발명에 따른 제조장치의 주요부를 확대하여 나타내는 상세도.
1 is a flowchart schematically illustrating a manufacturing process according to the present invention as a whole.
Figure 2 is a perspective view showing the entire manufacturing apparatus according to the present invention.
Figure 3 is a manufacturing state diagram showing the operation of the manufacturing apparatus according to the present invention.
4 and 5 are detailed views showing enlarged main parts of the manufacturing apparatus according to the present invention.

이하, 첨부도면을 참고하여 본 발명의 구성 및 이로 인한 작용, 효과에 대해 일괄적으로 기술하기로 한다.Hereinafter, with reference to the accompanying drawings, the configuration of the present invention and the actions and effects thereof will be described collectively.

본 발명의 이점 및 특징, 그리고 그것들을 달성하는 방법은 첨부되는 도면과 함께 상세하게 후술되어 있는 실시 예를 참조하면 명확해질 것이다. 그러나 본 발명은 이하에서 개시되는 실시 예에 한정되는 것이 아니라, 서로 다른 다양한 형태로 구현될 수 있으며, 단지 본 실시 예는 본 발명의 개시가 완전하도록 하고, 본 발명이 속하는 기술 분야에서 통상의 지식을 가진 자에게 발명의 범주를 완전하게 알려주기 위해 제공되는 것이며, 본 발명은 청구항의 범주에 의해 정의될 뿐이다. 그리고 명세서 전문에 걸쳐 동일 참조 부호는 동일 구성요소를 지칭한다.Advantages and features of the present invention, and a method of achieving them will become apparent with reference to embodiments described later in detail together with the accompanying drawings. However, the present invention is not limited to the embodiments disclosed below, but may be implemented in a variety of different forms, and only this embodiment is intended to complete the disclosure of the present invention, and common knowledge in the technical field to which the present invention pertains. It is provided to completely inform the scope of the invention to those who have, and the invention is only defined by the scope of the claims. In addition, the same reference numerals refer to the same elements throughout the entire specification.

본 발명은 펄프 재질의 습윤강력지 티슈 또는 기저귀 및 생리대 따위의 폐 위생용품을 이용하여 친환경 퇴비를 제조하는 방법과 관련되며, 도 1처럼 전처리단계(S10), 혼합단계(S20), 곤죽단계(S30), 부숙단계(S40)를 순차적으로 거쳐 친환경 퇴비를 제조하는 방법이다. The present invention relates to a method for producing an eco-friendly compost using a pulp-made wet strong paper tissue or waste hygiene products such as diapers and sanitary napkins, as shown in FIG. 1 , a pre-treatment step (S10), a mixing step (S20), a kneading step ( S30), it is a method of manufacturing an eco-friendly compost by sequentially passing through the fermentation step (S40).

본 발명의 제조방법 및 친환경 퇴비는 폐 위생용품을 재활용함으로써 원가의 절감으로 제조에 소요되는 전반적인 비용을 절감할 수 있을 뿐만 아니라 환경오염방지에 이바지할 수 있을 뿐만 아니라 탁월한 미생물로 인한 병원성 유해 곰팡이를 억제함으로써 고품질의 작물생장을 기대할 수 있는 것을 주요 요지로 한다.The manufacturing method and eco-friendly compost of the present invention can not only reduce the overall cost of manufacturing by reducing costs by recycling waste sanitary products, but also contribute to the prevention of environmental pollution, as well as prevent pathogenic harmful mold caused by excellent microorganisms. The main point is to be able to expect high-quality crop growth by suppressing it.

<전처리단계(S10)><Pre-processing step (S10)>

전처리단계(S10)는 준비된 폐 위생용품을 선별·세척·세절하여 주원료를 준비하는 과정이다. 즉, 준비된 폐 위생용품 중 불량 판정된 위생용품과 사용된 오염 위생용품을 분리한다. 그리고 분리된 오염 위생용품을 세척하여 이물질을 제거하면서 함유된 흡수성수지의 물 흡수를 억제 처리한다. 이어서 불량 판정된 위생용품과 세척 처리된 위생용품을 1~5㎜ 크기로 세절하는 과정을 거친다.The pretreatment step (S10) is a process of preparing the main raw material by screening, washing, and shredding the prepared waste hygiene products. That is, among the prepared waste hygiene products, the sanitary products determined to be defective and the used contaminated hygiene products are separated. Then, the water absorption of the water absorbent resin contained is suppressed while removing foreign substances by washing the separated contaminated sanitary products. Then, the sanitary products judged to be defective and the washed sanitary products are cut into pieces of 1-5 mm in size.

이때, 분리된 오염 위생용품은 물 70~90 중량%와 염화칼슘 30~10중량%가 혼합된 흡수억제제에 침지시켜 이물질을 제거하면서 함유된 고 흡수성수지(Super Absorbent Polymer)의 물 흡수를 억제 처리한다.At this time, the separated contaminated hygiene products are immersed in an absorption inhibitor mixed with 70 to 90% by weight of water and 30 to 10% by weight of calcium chloride to remove foreign substances while suppressing water absorption of the contained super absorbent polymer. .

즉, 물과 염화칼슘이 일정비율로 혼합된 흡수억제제는 고분자인 고 흡수성수지를 저분자 물질로 분해하여 물에 대한 용해성을 갖도록 하는 염화칼슘을 이용함으로써, 폐 위생용품에 포함된 고 흡수성수지가 일부 분해되도록 하여 저렴한 비용으로 흡수력을 낮추는 효과를 얻을 수 있다.In other words, the absorption inhibitor, in which water and calcium chloride are mixed in a certain ratio, uses calcium chloride, which decomposes the high water absorbent polymer, which is a high molecular weight, into a low molecular material to have solubility in water, so that the super absorbent polymer contained in the waste hygiene product is partially decomposed. Thus, it is possible to obtain the effect of lowering the absorption power at a low cost.

여기서 염화칼슘의 비율이 10 중량% 미만이면, 고 흡수성수지에 대한 흡수억제력이 미약하고, 30 중량%를 초과하면 염화칼슘의 농도가 지나치게 높아져 과도한 양의 염화칼슘이 퇴비에 포함되는 문제가 발생하므로 물 70~90 중량%와 염화칼슘 10~30 중량%의 비율을 갖게 하는 것이 바람직하다.Here, if the proportion of calcium chloride is less than 10% by weight, the absorption inhibitory power of the super absorbent polymer is weak, and if it exceeds 30% by weight, the concentration of calcium chloride becomes excessively high, and an excessive amount of calcium chloride is included in the compost. It is preferable to have a ratio of 90% by weight and 10 to 30% by weight of calcium chloride.

물론, 언급된 흡수억제제 외에도 스타취(starch)계, 셀룰로스(cellulose)계 또는 폴리아크릴산염(polyacrylic acid salt)계, 폴리비닐 알코올(polyvinyl alcohol)계, 폴리아크릴아마이드(polyacrylamide)계 및 폴리옥시에틸렌(polyoxyethylene)계 등의 합성수지계 등으로 조성할 수 있다.Of course, in addition to the aforementioned absorption inhibitors, starch-based, cellulose-based or polyacrylic acid salt-based, polyvinyl alcohol-based, polyacrylamide-based and polyoxyethylene It can be composed of synthetic resins such as (polyoxyethylene).

<혼합단계(S20)><Mixing step (S20)>

혼합단계(S20)는 준비된 주원료에 파쇄 처리된 산림부산물을 첨가하여 퇴비원료를 생성하는 과정이다. 즉, 전처리단계(S10)에서 준비된 주원료 70~90 중량%에 열가소성수지 10~30 중량%를 혼합한다. 바람직하게는 주원료 80 중량%에 분말 처리된 열가소성수지 20 중량%를 혼합하는 것이 좋다. 그리고 주원료와 열가소성수지 혼합물에 1~5㎜로 파쇄 처리된 나뭇가지와 톱밥 따위의 산림부산물을 1:1 중량비로 첨가한 이후 교반시켜 퇴비원료를 생성한다.The mixing step (S20) is a process of generating a compost raw material by adding the crushed forest by-products to the prepared main raw material. That is, 10 to 30% by weight of the thermoplastic resin is mixed with 70 to 90% by weight of the main raw material prepared in the pretreatment step (S10). Preferably, it is good to mix 20% by weight of the powder-treated thermoplastic resin with 80% by weight of the main raw material. And after adding forest by-products such as tree branches and sawdust crushed to 1-5 mm to the mixture of the main raw material and the thermoplastic resin in a 1:1 weight ratio, the mixture is stirred to produce a compost raw material.

이때, 열가소성수지는 폴리염화비닐(poly vinyl chloride), 폴리스티렌(polystyrene), 폴리에틸렌(polyethylene), 폴리프로필렌(polypropylene), 아크릴(acrylic), 폴리아미드(polyamide)수지 중 어느 하나 또는 복합적으로 조성될 수 있다. 이러한 열가소성수지는 재활용 처리된 것을 이용하여 환경보호를 도모하는 것이 좋다.At this time, the thermoplastic resin may be any one or a composite composition of polyvinyl chloride, polystyrene, polyethylene, polypropylene, acrylic, and polyamide resins. have. It is good to promote environmental protection by using such a thermoplastic resin that has been recycled.

<곤죽단계(S30)><Konjuk step (S30)>

곤죽단계(S30)는 생성된 퇴비원료에 미생물이 함유된 효소 액을 첨가하여 슬러지 상태로 조정하는 과정이다. 즉, 10% 염도를 가진 물 25L에 접종된 미생물이 37℃에서 3~5일간 배양된 효소 액을 혼합단계(S20)에서 생성된 퇴비원료에 첨가하여 pH 6.5~7.5 수분함수율 65~70%의 슬러지 상태로 조정한다. 여기서 효소 액은 미생물 배양된 물 25 중량%에 당밀 25 중량%, 비트펄프 20 중량%, 제올라이트 30 중량%가 첨가될 수 있다. 이 경우에는 퇴비원료의 수분함수율을 위해 물이 더 첨가된다.Konjuk step (S30) is a process of adjusting the sludge state by adding an enzyme solution containing microorganisms to the produced compost raw material. That is, the enzyme solution inoculated in 25L of water with 10% salinity is cultured at 37°C for 3 to 5 days and added to the composting material produced in the mixing step (S20), pH 6.5 to 7.5, moisture content of 65 to 70% Adjust to sludge condition. Here, the enzyme solution may include 25% by weight of molasses, 20% by weight of beet pulp, and 30% by weight of zeolite to 25% by weight of microbial cultured water. In this case, more water is added to increase the moisture content of the compost material.

이때, 미생물은 호기적 혐기적 상태에서 성장이 가능한 바실러스 리케니포르미스균 (Bacillus licheniformis), 바실러스 서브틸리스균 (Bacillus subtilis), 바실러스 스테아로스모필러스균 (Bacillus stearothermophillus) 중 어느 하나 또는 둘 이상 복합적으로 조성될 수 있다. 즉, 토양에서 추출한 미생물을 agar이 첨가된 Nutrient Broth 배지에 보관된 것을 이용한다.At this time, the microorganism is any one or a combination of two or more of Bacillus licheniformis, Bacillus subtilis, and Bacillus stearothermophillus that can grow in anaerobic anaerobic conditions can be composed of That is, the microorganisms extracted from the soil are stored in Nutrient Broth medium to which agar is added.

<부숙단계(S40)><Stage to stay (S40)>

부숙단계(S40)는 슬러지로 조정된 퇴비원료를 32~38℃에서 1 내지 3일간 발효시켜 퇴비화 시키는 과정이다. 즉, 곤죽단계(S30)에서 슬러지로 조정된 퇴비원료를 밀폐된 교반기에 투입하여 35℃의 열풍을 1~2시간마다 1~2분 동안 공급하면서 24시간마다 3~6회 텀블링시킨다. 바람직하게는 5℃의 열풍을 1시간마다 2분 동안 공급하면서 24시간 마다 5회 텀블링시키는 것이 좋다.The fermentation step (S40) is a process of composting the compost raw material adjusted to sludge by fermenting it at 32~38℃ for 1 to 3 days. That is, the compost raw material adjusted to the sludge in the kneading step (S30) is put into a sealed agitator and tumbled 3 to 6 times every 24 hours while supplying hot air at 35° C. for 1 to 2 minutes every 1 to 2 hours. Preferably, it is good to tumble 5 times every 24 hours while supplying hot air at 5° C. for 2 minutes every hour.

이러한 과정으로 제조된 퇴비는 수분함수율 40~50%를 지니고, 그램(g)당 바실러스 속(Bacillus spp) 1.4×107, 유산균(Lactic acid bacteria) 1.4×107로 함유된다. 따라서 부숙조건과 효소 액으로 우수한 퇴비화로 인해 미생물로 인한 병원성 유해 곰팡이를 억제함으로써 고품질의 작물생장을 기대할 수 있다.The compost produced by this process has a moisture content of 40-50% and contains 1.4×10 7 Bacillus spp and 1.4×10 7 Lactic acid bacteria per gram (g). Therefore, high quality crop growth can be expected by suppressing pathogenic and harmful mold caused by microorganisms due to excellent composting conditions and enzyme solution.

이때, 본 발명에 의해 완성된 폐 위생용품 퇴비 총 중량에 대해 커피부산물과 첨가물이 1:1 중량비로 혼합된 커피부산물 퇴비를 30~50% 배합할 수도 있다. 여기서 커피부산물은 외부와 밀폐된 건조기에서 청결된 상태로 완전 건조된 것을 이용한다.At this time, 30-50% of coffee by-product compost in which coffee by-products and additives are mixed in a 1:1 weight ratio with respect to the total weight of the waste sanitary product compost completed by the present invention may be blended. Here, coffee by-products are used that have been completely dried in a clean state in an external and sealed dryer.

그리고 첨가물로는 우유, 요구르트, 막걸리, 쌀뜨물 중 어느 하나 또는 둘 이상 혼합된 것을 사용한다. 이러한 커피부산물 퇴비는 N, K, Ca, Ma, P의 5가지 다량 원소와 Cu, Fe, Zn, Mn의 4가지 미량 원소가 함유되어 있다.And as an additive, any one or a mixture of two or more of milk, yogurt, makgeolli, and rice water is used. This coffee by-product compost contains five major elements of N, K, Ca, Ma, and P and four trace elements of Cu, Fe, Zn, and Mn.

따라서 중성토양에서 작물이 이용할 수 있는 다량원소가 들어 있어 작물이 양분을 흡수하는 역할을 도모하고, 환경 폐기물인 커피 부산물의 재활용으로 인해 환경오염을 방지할 수 있다.Therefore, it is possible to prevent environmental pollution by recycling coffee by-products, which are environmental wastes, as it contains a large amount of elements that can be used by crops in neutral soil.

한편, 본 발명의 교반기는 도 2처럼 설정 용량의 퇴비원료를 수용 가능한 크기를 가지는 프레임(10)과, 프레임(10)의 상단에 힌지(H)를 따라 회전 가능하게 배치되는 교반탱크(20)와, 교반탱크(20)의 내부 중앙에 모터(M)로부터 동력을 전달받아 회전하는 교반오거(30)와, 프레임(10)에 배치되어 교반탱크(20)를 좌우로 유동시키는 교반실린더(40)로 이루어진 것을 이용하는 것이 좋다.On the other hand, the stirrer of the present invention is a frame 10 having a size that can accommodate a compost raw material of a set capacity as shown in FIG. 2, and a stirring tank 20 that is rotatably disposed along a hinge H at the upper end of the frame 10. And, a stirring auger 30 that rotates by receiving power from the motor M in the center of the stirring tank 20, and a stirring cylinder 40 disposed in the frame 10 to flow the stirring tank 20 to the left and right ) is better to use.

이러한 교반기는 도면으로 도시하지 않았지만, 교반탱크(20)의 상단에 개폐되는 덮개와, 덮개 상에 열풍을 공급 순환시키는 배관 및 교반탱크(20)내외로 퇴비원료를 공급/배출하는 스크루 컨베이어를 포함한다.Although not shown in the drawings, this agitator includes a cover that opens and closes at the top of the stirring tank 20, a pipe for supplying and circulating hot air on the cover, and a screw conveyor for supplying/discharging compost material into and out of the stirring tank 20 do.

즉, 퇴비원료가 교반탱크(20)에 공급되면, 설정 타이머에 따라 교반오거(30)가 회전하며 내부로 열풍이 순환된다. 그리고 교반실린더(40)가 작동하여 도 3과 같이 교반탱크(20)에 진동과 함께 좌우로 유동시켜 퇴비원료를 텀블링 시킨다.That is, when the compost raw material is supplied to the stirring tank 20, the stirring auger 30 rotates according to the set timer and the hot air is circulated inside. And the agitation cylinder 40 is operated to flow left and right with vibration in the stirring tank 20 as shown in FIG. 3 to tumble the compost raw material.

여기서 교반오거(30)는 리본타입 또는 아바타입으로 구성할 수 있다. 리본타입은 도 4와 같이 교반 축(31)의 외면에 나선형으로 감겨지는 교반날개(35)가 각각 정역방향으로 배열된다. 이러한 리본타입 교반오거(30)는 퇴비원료를 교반 축(31) 방향으로 좌우 연속 이동시키며 혼합한다.Here, the stirring auger 30 may be configured as a ribbon type or an avatar type. In the ribbon type, the stirring blades 35 spirally wound on the outer surface of the stirring shaft 31 are arranged in the forward and reverse directions, respectively, as shown in FIG. 4 . This ribbon-type stirring auger 30 mixes the compost raw material while continuously moving left and right in the direction of the stirring shaft 31 .

그리고 아바타입은 도 5처럼 교반 축(31)의 외면에 소정 각도로 경사진 패들로 구성된 교반날개(35)가 방사형과 함께 축 방향으로 복수로 배열된다. 이러한 아바타입 교반오거(30)는 퇴비원료를 회전축(31)의 수직하는 회전방향으로 이동시키며 혼합한다.And as shown in FIG. 5, the stirring blades 35 composed of paddles inclined at a predetermined angle on the outer surface of the stirring shaft 31 are arranged radially and in plurality in the axial direction. The avatar-type stirring auger 30 moves and mixes the compost raw material in the direction of rotation perpendicular to the rotation shaft 31 .

이하, 본 발명에 따른 퇴비의 제조방법과 이에 제조된 퇴비의 효과를 입증하기 위해 아래와 같이 실험을 해보았다.Hereinafter, in order to prove the effect of the method for manufacturing compost according to the present invention and the compost prepared therefor, an experiment was conducted as follows.

<실험방법><Experiment method>

본 발명에 의해 제조된 퇴비(실시예)와 시중에 판매되는 퇴비(비교예)에 대해 식물 병원성 곰팡이 억제력과 균수 및 토마토 작물의 수확량을 알아보고자 한다.To investigate the plant pathogenic fungal inhibitory ability, the number of bacteria and the yield of tomato crops for the compost prepared by the present invention (Example) and commercially available compost (Comparative Example).

<시료제작><Sample production>

10% 염도를 가진 물 25L에 미생물이 37℃에서 3일간 배양된 상태에서 당밀 25㎏, 비트펄프 25㎏, 제올라이트 35㎏을 혼합한 효소 액과 물을 퇴비원료와 배합하여 수분함수율 68% 슬러지 상태로 조정한 다음, 교반기에서 35℃의 열풍을 1시간마다 2분 동안 공급하면서 24시간 마다 5회 텀블링하는 과정으로 3일간 부숙하여 퇴비를 완성하였다. 여기서 효소 액은 바실러스 리케니포르미스균(실시예1), 바실러스 서브틸리스균(실시예2), 바실러스 스테아로스모필러스균(실시예3)으로 구분하여 각각 별도로 완성하였다.In 25L of water with 10% salinity, in a state where microorganisms were cultured at 37°C for 3 days, an enzyme solution mixed with 25 kg of molasses, 25 kg of beet pulp, and 35 kg of zeolite was mixed with compost, and water content was 68% sludge. , and then tumbled 5 times every 24 hours while supplying hot air at 35° C. from the stirrer for 2 minutes every hour to complete compost for 3 days. Here, the enzyme solution was divided into Bacillus licheniformis (Example 1), Bacillus subtilis (Example 2), and Bacillus stearosmophilus (Example 3), and each was completed separately.

<식물 병원성 곰팡이 억제력 평가><Evaluation of plant pathogenic fungal inhibitory power>

식물 병원성 곰팡이인 Rhizopus stronifer 균체를 YM agar plate에 중층한 후 멸균된 paper disc를 위에 올려놓고, 실시예1 내지 실시예3과 비교예 퇴비 20㎕씩 paper disc에 적하한 다음 agar plate를 30℃에서 5일간 배양한 후 저해환의 크기를 측정하였다.After layering the Rhizopus stronifer cells, a plant pathogenic fungus, on a YM agar plate, put a sterilized paper disc on top, and 20 μl of each of Examples 1 to 3 and Comparative Example compost was dropped onto the paper disc, and then the agar plate was placed at 30°C After culturing for 5 days, the size of the inhibition ring was measured.

<퇴비 균수 및 균종 분석><Analysis of number and species of compost>

실시예1 내지 실시예3과 비교예의 퇴비 100㎎을 9㎖ 생리식염수에 10-10~10-8 배율로 연속 희석하여 YM agar plate에 도말하여 37℃에서 3일간 배양한 후 균수 및 균종을 분석하였다.100 mg of the compost of Examples 1 to 3 and Comparative Example was serially diluted in 9 ml of physiological saline at a 10 -10 to 10 -8 fold, spread on a YM agar plate, and cultured at 37° C. for 3 days, and then the number and species of bacteria were analyzed. did.

<퇴비에 대한 작물시험><Crop test on compost>

토마토 밭에서 파종시부터 1달 주기로 밭흙에 실시예1 내지 실시예3과 비교예 퇴비를 각각 살포하고 최종적으로 작물 수확량을 비교하였다.From the time of sowing in the tomato field, the compost of Examples 1 to 3 and Comparative Example was respectively sprayed on the soil at a one-month cycle, and finally the crop yields were compared.

<식물 병원성 곰팡이 억제력 평가 결과><Result of evaluation of phytopathogenic fungal inhibitory ability>

구분division 저해환 크기(㎜)Inhibitory ring size (mm) 실시예1Example 1 1818 실시예2Example 2 1919 실시예3Example 3 3030 비교예Comparative example 1212

식물 병원성 곰팡이 Rhizopus stronifer에 대한 성장 억제력을 평가한 결과, 모든 퇴비가 곰팡이 성장에 억제력이 나타났다. 그러나 저해환의 크기로 억제성능을 살펴보면, 표 1과 같이 대체적으로 실시예가 비교예 보다 우수하였으며 그 중에서 바실러스 스테아로스모필러스균인 실시예3이 가장 탁월한 것을 알 수 있다.As a result of evaluating the growth inhibitory ability against the phytopathogenic fungus Rhizopus stronifer, all composts showed inhibitory activity on the fungal growth. However, looking at the inhibitory performance by the size of the inhibitory ring, as shown in Table 1, Examples were generally superior to Comparative Examples, and among them, Example 3, which is Bacillus stearosmophilus, was the most excellent.

<퇴비 균수 및 균종 분석 결과><Result of compost bacteria count and species analysis>

구분division 세포 수(108 cell/g)Number of cells (10 8 cells/g) 실시예1Example 1 7.57.5 실시예2Example 2 3.53.5 실시예3Example 3 2.02.0 비교예Comparative example 1.21.2

퇴비에 대한 균수와 균종을 분석한 결과, 모든 퇴비에서 바실러스 속(Bacillus spp), 유산균(Lactic acid bacteria)이 발견되었다. 그러나 그램(g)당 세포 수는 표 2와 같이 대체적으로 실시예가 비교예 보다 우수하였으며 그 중에서 바실러스 리케니포르미스균인 실시예1이 가장 높은 것을 알 수 있다.As a result of analyzing the number and types of bacteria in the compost, Bacillus spp and Lactic acid bacteria were found in all composts. However, as shown in Table 2, the number of cells per gram (g) was generally superior to that of Comparative Example, and it can be seen that Example 1, which is Bacillus licheniformis, was the highest among them.

<퇴비에 대한 작물시험 결과><Result of crop test on compost>

구분division 수확량 (㎏)Yield (kg) 상대적 수확량 (%)Relative Yield (%) 실시예1Example 1 37.537.5 129129 실시예2Example 2 40.140.1 137137 실시예3Example 3 36.536.5 125125 비교예Comparative example 29.029.0 100100

퇴비에 대한 작물시험 결과, 동 면적대비 수확량이 표 3과 같이 비교예 보다 실시예가 최소 25에서 최대 37 수확 증산 율로 나타났다. 그 중에서 바실러스 서브틸리스균인 실시예2의 수확량이 가장 높은 것을 알 수 있다.As a result of the crop test on compost, as shown in Table 3, the yield compared to the same area was increased in the Example from a minimum of 25 to a maximum of 37 compared to the Comparative Example. Among them, it can be seen that the yield of Example 2, which is Bacillus subtilis, is the highest.

이와 같이 본 발명은 폐 위생용품을 재활용함으로써 원가의 절감으로 제조에 소요되는 전반적인 비용을 절감할 수 있을 뿐만 아니라 환경오염방지에 이바지할 수 있고, 위생용품에 함유된 고 흡수성수지 기능을 보다 저렴한 비용으로 제작된 흡수억제제를 통해 억제 처리함으로써 퇴비의 가격경쟁력을 도모할 수 있다. 그리고 한 달에서 두 달 이상 소요되는 부숙기간을 현저히 단축하면서도 위생용품의 속성 대량처리와 함께 퇴비의 속성 대량생산이 가능할 뿐만 아니라 부숙조건과 효소 액으로 우수한 퇴비화로 인한 미생물로 병원성 유해 곰팡이를 억제함으로써 고품질의 작물생장을 기대할 수 있다.As described above, the present invention can reduce the overall cost of manufacturing by recycling waste sanitary products, as well as contribute to the prevention of environmental pollution, and reduce the cost of the super absorbent polymer contained in sanitary products at a lower cost. It is possible to promote the price competitiveness of compost by suppressing treatment through absorption inhibitors produced with And while remarkably shortening the fermentation period, which takes one to two months, it is possible to mass-produce the properties of compost along with the property mass processing of sanitary products, as well as suppress pathogenic harmful molds with microorganisms due to excellent composting conditions and enzyme solutions High-quality crop growth can be expected.

H: 힌지 M: 모터
10: 프레임 20: 교반탱크
30: 교반오거 31: 교반축
35: 날개 40: 교반실린더
S10: 전처리단계
S20: 혼합단계
S30: 곤죽단계
S40: 부숙단계
H: Hinge M: Motor
10: frame 20: stirred tank
30: stirring auger 31: stirring shaft
35: wing 40: stirring cylinder
S10: pre-processing step
S20: mixing step
S30: Konjuk stage
S40: Fertility stage

Claims (3)

폐 위생용품을 이용한 친환경 퇴비를 제조하는 방법에 있어서,
준비된 폐 위생용품을 선별·세척·세절하여 주원료를 준비하는 전처리단계(S10);
전 처리단계에서 준비된 주원료 70-90중량%에 폴리염화비닐, 폴리스틸렌, 폴리에틸렌, 폴리프로필렌, 아크릴, 폴리아미드 수지 중 어느 하나 또는 복합적으로 조성되는 열가소성 수지 10-30중량%을 혼합하여 열가소성 수지에 산림부산물을 1:1 중량비로 첨가한 후 교반시켜서 생성하는 혼합단계(S20);
생성된 퇴비원료에 미생물이 함유된 효소 액을 첨가하여 슬러지 상태로 조정하는 곤죽단계(S30);
슬러지로 조정된 퇴비원료를 32~38℃에서 1 내지 3일간 발효시켜 퇴비화 시키는 부숙단계(S40);
를 포함하되,
상기 곤죽단계(S30)는 10% 염도를 가진 물 25L에 접종된 미생물이 37℃에서 3~5일간 배양된 효소 액을 첨가하여 pH 6.5~7.5 수분함수율 65~70%의 슬러지 상태로 조정하는 것을 특징으로 하는 폐 위생용품을 이용한 친환경 퇴비의 제조방법.


In the method of manufacturing an eco-friendly compost using waste hygiene products,
A pre-processing step (S10) of preparing a main raw material by screening, washing, and slicing the prepared waste hygiene products;
Polyvinyl chloride, polystyrene, polyethylene, polypropylene, acrylic, polyamide resin, or any one of polyvinyl chloride, polystyrene, polyethylene, polypropylene, acryl, and polyamide resin, or 10-30 wt% of a composite composition by mixing 70-90 wt% of the main raw material prepared in the pre-treatment step A mixing step (S20) of adding by-products in a 1:1 weight ratio and then stirring to produce;
Konjuk step (S30) of adjusting the sludge state by adding an enzyme solution containing microorganisms to the produced compost raw material;
Fermenting the compost raw material adjusted to sludge at 32~38℃ for 1 to 3 days to compost it (S40);
Including,
The kneading step (S30) is to adjust the sludge state of pH 6.5-7.5 moisture content of 65-70% by adding the enzyme solution in which the microorganisms inoculated in 25L of water with 10% salinity are cultured at 37°C for 3-5 days. A method of manufacturing eco-friendly compost using waste sanitary products.


삭제delete 제1항에 의한 방법으로 제조된 퇴비는 수분함수율 40~50%를 지니고, 그램(g)당 바실러스 속(Bacillus spp) 1.4×107, 유산균(Lactic acid bacteria) 1.4×107로 함유된 것을 특징으로 하는 폐 위생용품을 이용한 친환경 퇴비.The compost prepared by the method according to claim 1 has a moisture content of 40-50% and contains 1.4×10 7 Bacillus spp and 1.4×10 7 Lactic acid bacteria per gram (g). Eco-friendly compost using waste hygiene products.
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