KR20200120481A - Loess fermentation strain composition for water purification and water purification method using the same - Google Patents

Loess fermentation strain composition for water purification and water purification method using the same Download PDF

Info

Publication number
KR20200120481A
KR20200120481A KR1020190167362A KR20190167362A KR20200120481A KR 20200120481 A KR20200120481 A KR 20200120481A KR 1020190167362 A KR1020190167362 A KR 1020190167362A KR 20190167362 A KR20190167362 A KR 20190167362A KR 20200120481 A KR20200120481 A KR 20200120481A
Authority
KR
South Korea
Prior art keywords
strain
loess
weight
parts
water purification
Prior art date
Application number
KR1020190167362A
Other languages
Korean (ko)
Inventor
하동길
Original Assignee
(주)미래연바이오텍
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 (주)미래연바이오텍 filed Critical (주)미래연바이오텍
Priority to KR1020190167362A priority Critical patent/KR20200120481A/en
Publication of KR20200120481A publication Critical patent/KR20200120481A/en
Priority to KR1020210101510A priority patent/KR20210105849A/en

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/20Bacteria; Culture media therefor

Abstract

The present invention is to purify the water quality of contaminated rivers, reservoirs, or freshwater lakes using a loess fermentation strain composition for water purification. The loess fermentation strain composition for water purification of the present invention includes 50 to 150 parts by weight of a liquefied strain mixed with 100 parts by weight of loess to produce a loess strain for water purification, and is fermented by putting the loess strain in a sealed container for 50 to 80 days at 30 to 35°C. In addition, the liquefied strain is mixed with 1 to 5 parts by weight of a Bacillus strain or 2 to 7 parts by weight of a strain of Paenibacillus in 100 parts by weight of water, and is cultured at 32 to 37°C for 24 to 48 hours. A water purification method using the loess fermentation strain composition for water purification of the present invention provides an effect of quickly purifying contaminated water in rivers or reservoirs and freshwater lakes at low cost.

Description

수질 정화용 황토발효 균주 조성물 및 이를 이용한 수질정화방법{.}Yellow soil fermentation strain composition for water purification and water purification method using the same{.}

본 발명은 수질 정화용 황토발효 균주 조성물을 이용한 수질정화방법에 관한 것으로 것으로, 구체적으로는 균주를 황토에 배양하고 숙성 발효시켜 수질 정화용 황토발효 균주 조성물을 제조하고, 이를 이용하여 저수지, 담수호 또는 하천의 오염수를 정화처리하는 방법에 관한 것이다.The present invention relates to a water purification method using a composition of a fermented loess strain for water purification, and specifically, a strain is cultured in loess and fermented by fermentation to prepare a loess-fermented strain composition for water purification, and the composition is used in a reservoir, a freshwater lake, or a river. It relates to a method of purifying contaminated water.

근래 인간 활동이 다변화하고, 농업, 축산 등 산업활동이 증가됨에 따라 축산폐수, 농업 오염수, 생활하수 및 폐수 등이 하천이나 저수지, 담수호 등으로 유입돼 수질환경의 오염을 유발시키는 경우가 자주 발생되고 있다.In recent years, as human activities have diversified and industrial activities such as agriculture and livestock increase, livestock wastewater, agricultural contaminated water, domestic sewage and wastewater flow into rivers, reservoirs, and freshwater lakes, causing pollution of the water quality. Has become.

하천이나 저수지 또는 담수호 등의 오염을 감소시키려면 유입되는 오염원을 원천적으로 차단하여야 한다. 오염원을 차단하지 못하여 하천 또는 저수지 등이 오염되는 경우에는 오염된 하천 등의 물을 인위적으로 처리하여야 한다.In order to reduce pollution of rivers, reservoirs, or freshwater lakes, the inflow of pollutants must be fundamentally blocked. If a river or reservoir is contaminated due to failure to block the pollutant source, water from the contaminated river must be artificially treated.

하천 등의 수질을 정화시키기 위해서 물리화학적인 방법으로 오염된 수질을 정화시켜야 하며, 이러한 오염수 처리공정은 고도처리 시설 등의 설비가 필요하고 많은 비용이 소요될 수 있다. 또한 담수호 또는 저수지 등의 수질이 오염되면 수질 정화시설을 설치하는 것도 쉽지 않은 문제점이 있다.In order to purify the quality of water such as rivers, contaminated water must be purified by a physicochemical method, and such a contaminated water treatment process requires facilities such as advanced treatment facilities and can be costly. In addition, if the water quality of a freshwater lake or reservoir is contaminated, it is not easy to install a water purification facility.

최근에는 이러한 하천 등의 오염수를 처리하기 위해 다양한 방법들이 개발되고 있으나, 쉽게 처리되지 않아 수질환경이 악화되고 있는 실정이다. 즉, 오염수에 혼합되어 있는 질소, 인, 중금속 등 오염물질를 흡수 제거하거나, 수질 정화식물을 이용하여 친환경적인 수질 정화방법 등의 노력이 강구되고 있으나, 크게 효과를 거두지는 못하고 있다.Recently, various methods have been developed to treat contaminated water such as rivers, but the water quality environment is deteriorating because they are not easily treated. That is, efforts are being made to absorb and remove pollutants such as nitrogen, phosphorus, and heavy metals mixed in the contaminated water, or to use an eco-friendly water purification method using a water purification plant, but it has not been greatly effective.

국내 등록특허공보 제10-11005408호(2015. 10. 02)Korean Patent Publication No. 10-11005408 (2015. 10. 02)

본 발명은 상기와 같은 문제점을 해결하기 위한 것으로 오염된 하천, 저수지 또는 담수호 등의 수질을 황토발효 균주 조성물을 이용하여 정화시키기 위한 것이다.The present invention is to solve the above problems, and to purify the water quality of contaminated rivers, reservoirs, or freshwater lakes using a loess fermentation strain composition.

본원발명은 수질 정화용 황토발효 균주 조성물을 이용하여 오염된 담수호의 수질 또는 저수지의 바닥 퇴적토를 정화시키기 위한 것을 목적으로 한다.The present invention aims to purify the water quality of contaminated freshwater lakes or bottom sedimentary soil of a reservoir by using the loess fermentation strain composition for water purification.

또한 본원발명은 저수지 등의 오염수와 담수호 등의 퇴적토를 정화함에 있어서 수질 정화용 황토발효 균주 조성물을 이용하여 저렴한 비용으로 1차 수질정화 및 2차 퇴적물을 정화시키기 위한 방법을 제공한다.In addition, the present invention provides a method for purifying primary water quality and secondary sediment at low cost by using a loess fermentation strain composition for water purification in purifying contaminated water such as reservoirs and sediments such as freshwater lakes.

상기 목적을 달성하기 위해서, 본 발명에 따른 수질 정화용 황토발효 균주 조성물은 황토 100중량부에 액상화된 균주 50~150중량부를 혼합하여 수질 정화용 황토균주를 제조하고, 상기 황토균주를 밀폐된 용기에서 투입하여 발효시키되, 상기 발효 온도는 30~37℃에서 50~80일 동안 발효시킨다.In order to achieve the above object, the composition of the loess fermentation strain for water purification according to the present invention is prepared by mixing 50 to 150 parts by weight of the liquefied strain to 100 parts by weight of loess to prepare a loess strain for water purification, and the loess strain is put in a sealed container. And fermented, the fermentation temperature is 30 to 37 ℃ fermentation for 50 to 80 days.

상기 액상화된 균주는 물 100 중량부에 바실러스(Bacillus)속 균주 1~5중량부 또는 패니바실러스(Paenibacillus)속 균주 2~7중량부를 혼합하여 32~37℃에서 24~48시간 배양한 균주를 사용하다.The liquefied strain was mixed with 1 to 5 parts by weight of Bacillus sp. strain or 2 to 7 parts by weight of Paenibacillus strain in 100 parts by weight of water, and cultured at 32 to 37°C for 24 to 48 hours. Do.

상기 수질 정화용 황토발효 균주 조성물은 오염수에 투입하기 전에 숙성된 황토발효 균주 조성물의 황토는 0.005~0.03mm 크기이다. The loess-fermented strain composition for water purification has a size of 0.005 to 0.03 mm of loess in the loess-fermented strain composition aged before being added to contaminated water.

상기 수질 정화용 황토발효 균주 조성물은 오염수 1L에 상기 분말화한 황토발효 균주 조성물 10~100g의 비율로 혼합하여 저수지, 하천 또는 담수호의 오염된 수질을 정화한다.The loess fermentation strain composition for water purification is mixed in 1L of contaminated water at a ratio of 10 to 100g of the powdered loess fermentation strain composition to purify contaminated water quality of a reservoir, river or freshwater lake.

본 발명의 수질 정화용 황토발효 균주 조성물을 이용한 수질 정화방법은 하천 또는 저수지 및 담수호의 오염된 물을 저렴한 비용으로 신속하게 정화시켜 주는 효과를 제공한다. 또한 하천 또는 저수지 및 담수호 등에서 퇴적되는 퇴적토의 오염까지 정화시켜 주는 효과를 제공한다. 즉, 황토발효 균주 조성물에 사용되는 황토는 활성화된 균주의 영향으로 황토 내부가 부드럽게 연화되어 오염된 물과의 접촉면적이 증가되어 수질정화 효과가 탁월하고, 침전되는 침전물까지도 정화시켜 주는 효과가 있으며, 침전물은 비료 또는 농경지의 토양 개량제 등으로 사용할 수 있어 소득 증대 등의 효과를 제공한다. The water purification method using the loess fermentation strain composition for water purification of the present invention provides the effect of quickly purifying contaminated water in rivers or reservoirs and freshwater lakes at low cost. In addition, it provides the effect of purifying the contamination of sedimentary soil deposited in rivers or reservoirs and freshwater lakes. In other words, the loess used in the loess fermentation strain composition softly softens the loess inside under the influence of the activated strain, so that the contact area with contaminated water is increased, so that the water purification effect is excellent, and it has the effect of purifying even sediment. , Sediment can be used as a fertilizer or a soil conditioner for agricultural land, providing an effect of increasing income.

또한, 악취가 심한 오염수에 투입하는 경우 황토발효 균주의 활성으로 악취제거에 용이하여 오염 지역을 신속하게 정화할 수 있는 효과가 있다.In addition, when it is put into contaminated water with a severe odor, it is easy to remove odor due to the activity of the loess fermentation strain, and thus there is an effect of quickly purifying the contaminated area.

도 1은 본 발명의 황토발효 균주 조성물을 이용하여 오염된 수질의 처리 전후를 비교한 사진이다.1 is a photograph comparing before and after treatment of contaminated water using the loess fermentation strain composition of the present invention.

본 발명은 황토발효 균주 조성물을 이용한 수질정화방법에 관한 것이다.The present invention relates to a water purification method using the loess fermentation strain composition.

이하 도면 및 실시예를 이용하여 본 발명에 대하여 상세하게 설명하도록 한다. 도 1은 본 발명의 황토발효 균주 조성물을 이용하여 정화된 수질과 오염된 수질을 비교한 사진이다.Hereinafter, the present invention will be described in detail with reference to the drawings and examples. 1 is a picture comparing the quality of purified water and contaminated water using the loess fermentation strain composition of the present invention.

본 발명의 수질 정화용 황토발효 균주 조성물은 0.005~0.03mm 크기로 분말화된 황토 100중량부에 액상화된 균주 50~150중량부를 혼합하여 수질 정화용 황토균주를 제조하고, 상기 황토균주를 밀폐된 용기에서 투입하여 발효시킨다. 상기 밀폐된 용기에서 황토균주를 발효시키는 조건은 온도 30~37℃에서 50~80일 동안 발효 숙성시켜 황토발효 균주 조성물을 제조한다. The loess fermentation strain composition for water purification of the present invention is prepared by mixing 50 to 150 parts by weight of the liquefied strain with 100 parts by weight of powdered loess in a size of 0.005 to 0.03 mm to prepare a loess strain for water purification, and the loess strain in a sealed container. Put in and ferment. Conditions for fermenting the loess strain in the sealed container are fermented and aged at a temperature of 30 to 37° C. for 50 to 80 days to prepare a loess fermented strain composition.

상기 황토발효 균주 조성물을 오염수에 투입할 때에는 오염수 1L에 상기 분말화한 황토발효 균주 조성물 10~100g의 비율로 혼합하는 것이 바람직하다. 상기 오염수에 황토발효 균주 조성물을 혼합할 때 셀룰로오스 1~2중량부를 더 혼합하는 경우 오염된 수질의 정화를 촉진할 수 있으며, 상기 셀룰로오스를 추가하는 경우 수질 정화효율은 10~20% 더 증진된다.When the loess fermentation strain composition is added to contaminated water, it is preferable to mix the powdered loess fermentation strain composition in 1L of contaminated water in a ratio of 10 to 100 g. When mixing the loess fermentation strain composition with the contaminated water, when 1 to 2 parts by weight of cellulose is further mixed, purification of contaminated water can be promoted, and when the cellulose is added, the water purification efficiency is further improved by 10-20%. .

상기 액상화된 균주는 물 100 중량부에 바실러스(Bacillus)속 균주 1~5중량부 및/또는 패니바실러스(Paenibacillus)속 균주 2~7중량부를 혼합하여 32~40℃에서 24~48시간 배양한 균주를 사용한다. 상기 균주가 배양되는 물에는 포도당, 과당, 수크로스, 아미노산 등의 균주 영양분을 혼합하여 균주가 용이하게 번식 생육할 수 있도록 하며, 물 100 중량부에 상기 균주 영양분 5~10중량부의 비율로 혼합되는 것이 바람직하다. 균주 영양분이 10중량부 이상으로 혼합이 되면 초기에 과도하게 균주가 번식하고, 5중량부 이하로 혼합하는 경우 영양분에 대한 경쟁이 심해져서 균주의 배양이 더디게 된다. 또한 상기 물 100중량부에 혼합되는 바실러스 속 균주는 바실러스 트로피쿠스(Bacillus tropicus)이고, 패니바실러스 속 균주는 패니바실러스리오그랜덴시스(Paenibacillus riograndensis) 및 패니바실러스 동도넨시시(Paenibacillus dongdonensis KUDC0114) 균주를 사용한다.The liquefied strain is a strain cultured at 32 to 40°C for 24 to 48 hours by mixing 1 to 5 parts by weight of Bacillus strain and/or 2 to 7 parts by weight of the genus Paenibacillus strain to 100 parts by weight of water Use. The strain nutrients such as glucose, fructose, sucrose, and amino acids are mixed in the water in which the strain is cultured so that the strain can be easily reproduced and grown, and the strain nutrients are mixed in a ratio of 5 to 10 parts by weight to 100 parts by weight of water. It is desirable. When the nutrient of the strain is mixed in more than 10 parts by weight, the strain is excessively propagated initially, and when the nutrient is mixed in less than 5 parts by weight, competition for nutrients intensifies and the cultivation of the strain is slow. In addition, the strain of the genus Bacillus mixed with 100 parts by weight of water is Bacillus tropicus, and the strains of the genus Panibacillus are Paenibacillus riograndensis and Paenibacillus dongdonensis KUDC0114 strains Use.

상기 물 100중량부에 혼합되는 바실러스 속 균주 : 패니바실러스속 균주의 비율은 1: 1.5의 비율로 혼합하는 것이 바람직하며, 각각 사용하는 것도 가능하다.Bacillus strain mixed with 100 parts by weight of the water: Panibacillus strain is preferably mixed in a ratio of 1: 1.5, it is also possible to use each.

또한 상기 물 100중량부에 사용되는 균주는 바실러스 코리엔시스(Bacillus koriensi DSM16467)1~3중량부 및 브레비바실러스 니트리피칸스(Breviacillus nitrificans DA2) 1~4 중량부를 더 포함하여 배양하는 것도 가능하다.In addition, the strain used in 100 parts by weight of water may further include 1 to 3 parts by weight of Bacillus koriensi DSM16467 and 1 to 4 parts by weight of Breviacillus nitrificans DA2. .

<실시예><Example>

도 1에서 오른쪽 사진([2])은 생활 폐수 등으로 오염된 수질이며, 상기 [2]의 오염된 수질 100중량부에 상기 황토발효 균주 조성물 5중량부를 혼합한 다음 2일이 경과하여 오염된 물이 정화된 사진이 왼쪽사진([1])이다.In Figure 1, the photo on the right ([2]) is the quality of water contaminated with domestic wastewater, etc., and 5 parts by weight of the loess fermentation strain composition is mixed with 100 parts by weight of the contaminated water quality of [2], and then 2 days have elapsed. The picture of the purified water is the picture on the left ([1]).

즉, 상기와 같은 조건에서 오염된 수질에 황토발효균주 조성물을 처리하는 경우 오염물질의 80~95%가 제거되고, 오염된 물질이 제거된 상기 상등액은 무해하였으며, BOD가 0.5~1.0mg/L로 기준치 이하였다.That is, in the case of treating the loess fermentation strain composition in the contaminated water under the above conditions, 80-95% of the contaminants were removed, the supernatant from which the contaminated material was removed was harmless, and the BOD was 0.5-1.0 mg/L. Was below the standard value.

또한 COD는 1.0~2.0mg/L, 총질소(T-N)는 2.5mg/L, 총인(T-N)은 1.7mg/L로 크게 감소하였다.In addition, COD decreased significantly to 1.0~2.0mg/L, total nitrogen (T-N) 2.5mg/L, and total phosphorus (T-N) 1.7mg/L.

또한 황토는 적조생물 중 코클로디니움(Cochlodinium)의 제거에도 탁월한 효과를 제공한다. 즉, 코클로디니움으로 오염된 물 100중량부에 상기 황토발효 균주 조성물 1~10중량부를 투입하였을 때 적조생물 제거효과는 50~90% 제거되었으며, 황토발효 균주 조성물의 혼합 비율이 증가할수록 적조생물 제거에 효과적이다.In addition, loess provides excellent effects in the removal of Cochlodinium among red tide organisms. That is, when 1 to 10 parts by weight of the loess fermentation strain composition was added to 100 parts by weight of water contaminated with coclodinium, the effect of removing red tide organisms was removed by 50 to 90%, and as the mixing ratio of the loess fermented strain composition increased, effective.

상기 황토발효 균주 조성물 살포 30분후에 Cochlodinium 적조생물이 75-85% 제거되었으며, 수온 및 pH는 변화가 없고, 용존산소, 화학적 산소요구량 및 클로로필 a의 농도는 감소하였고 부유물질은 증가하였다. 부영양화인자중 용존무기인은 살포전후 농도변화가 없는 반면, 용존무기질소는 살포후가 살포전에 비해 다소 감소하였다. 황토발효 균주 조성물은 5~10중량부의 비율로 살포하였을 때 적조 생물 제거에 효과적이고, 오염된 수질도 크게 향상되었다.After 30 minutes of spraying the loess fermentation strain composition, 75-85% of Cochlodinium red tide organisms were removed, the water temperature and pH were not changed, dissolved oxygen, chemical oxygen demand and the concentration of chlorophyll a decreased, and suspended solids increased. Among eutrophication factors, dissolved inorganic phosphorus did not change in concentration before and after application, whereas dissolved inorganic nitrogen was slightly decreased after application compared to before application. The loess fermentation strain composition is effective in removing red tide organisms when sprayed at a ratio of 5 to 10 parts by weight, and contaminated water quality is also greatly improved.

Claims (2)

수질 정화용 황토발효 균주 조성물에 있어서,
상기 수질 정화용 황토발효 균주 조성물은 0.005~0.03mm 크기로 분말화된 황토 100중량부에 액상화된 균주 50~150중량부를 혼합하여 수질 정화용 황토균주를 제조하고,
상기 황토발효 균주를 밀폐된 용기에 투입하여 30~35℃에서 50~80일 동안 발효시켜 황토발효 균주 조성물을 제조하며,
상기 액상화된 균주는 균주의 영양분이 혼합된 물 100 중량부에 바실러스 트로피쿠스(Bacillus tropicus) 1~5중량부 및 패니바실러스(Paenibacillus)속 균주 2~7중량부를 혼합하여 32~37℃에서 24~48시간 배양한 균주를 사용하되, 상기 균주의 영양분으로 포도당, 과당, 수크로스, 아미노산이 5~10중량부의 비율로 혼합되며,
상기 패니바실러스 속 균주는 패니바실러스 리오그랜덴시스(Paenibacillus riograndensis) 또는 패니바실러스 동도넨시시(Paenibacillus dongdonensis KUDC0114)를 사용하며,
상기 수질 정화용 황토발효 균주 조성물을 이용하여 오염수를 처리할 때 상기 오염수 1L에 상기 수질 정화용 황토발효 균주 조성물 10~100g을 혼합하여 처리하되, 상기 오염수에 황토발효 균주 조성물을 혼합할 때 셀룰로오스 1~2중량부를 더 혼합하여 처리하는 것을 특징으로 하는 수질 정화용 황토발효 균주 조성물
In the loess fermentation strain composition for water purification,
The loess fermentation strain composition for water purification is prepared by mixing 50 to 150 parts by weight of the liquefied strain to 100 parts by weight of powdered loess in a size of 0.005 to 0.03 mm to prepare a loess strain for water purification,
The loess fermentation strain is put into a sealed container and fermented at 30 to 35° C. for 50 to 80 days to prepare a loess fermented strain composition,
The liquefied strain is a mixture of 1 to 5 parts by weight of Bacillus tropicus and 2 to 7 parts by weight of a strain of the genus Paenibacillus in 100 parts by weight of water in which the nutrients of the strain are mixed, and at 32 to 37°C, 24 to A strain cultured for 48 hours is used, but as nutrients of the strain, glucose, fructose, sucrose, and amino acids are mixed in a ratio of 5 to 10 parts by weight,
The strain of the genus Panibacillus is used as Panibacillus riograndensis or Paenibacillus dongdonensis KUDC0114,
When treating contaminated water using the water purification loess fermentation strain composition, 1L of the contaminated water is treated by mixing 10 to 100 g of the loess fermentation strain composition for water purification, but when the loess fermentation strain composition is mixed with the contaminated water, cellulose 1 to 2 parts by weight of the loess fermentation strain composition for water purification, characterized in that further mixing and treating
제1항에 있어서,
상기 액상화된 균주는 바실러스 코리엔시스(Bacillus koriensi DSM16467)1~3중량부 및 브레비바실러스 니트리피칸스(Breviacillus nitrificans DA2) 1~4 중량부를 더 포함하여 배양하는 것을 특징으로 하는 수질 정화용 황토발효 균주 조성물
The method of claim 1,
The liquefied strain is Bacillus koriensi (Bacillus koriensi DSM16467) 1 to 3 parts by weight and Breviacillus nitrificans (Breviacillus nitrificans DA2) 1 to 4 parts by weight further comprising a cultured loess fermentation strain for water purification Composition
KR1020190167362A 2019-12-16 2019-12-16 Loess fermentation strain composition for water purification and water purification method using the same KR20200120481A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
KR1020190167362A KR20200120481A (en) 2019-12-16 2019-12-16 Loess fermentation strain composition for water purification and water purification method using the same
KR1020210101510A KR20210105849A (en) 2019-12-16 2021-08-02 Yellow soil fermentation strain composition for water purification and water purification method using the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1020190167362A KR20200120481A (en) 2019-12-16 2019-12-16 Loess fermentation strain composition for water purification and water purification method using the same

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
KR1020190043330 Division 2019-04-12

Related Child Applications (1)

Application Number Title Priority Date Filing Date
KR1020210101510A Division KR20210105849A (en) 2019-12-16 2021-08-02 Yellow soil fermentation strain composition for water purification and water purification method using the same

Publications (1)

Publication Number Publication Date
KR20200120481A true KR20200120481A (en) 2020-10-21

Family

ID=73034921

Family Applications (2)

Application Number Title Priority Date Filing Date
KR1020190167362A KR20200120481A (en) 2019-12-16 2019-12-16 Loess fermentation strain composition for water purification and water purification method using the same
KR1020210101510A KR20210105849A (en) 2019-12-16 2021-08-02 Yellow soil fermentation strain composition for water purification and water purification method using the same

Family Applications After (1)

Application Number Title Priority Date Filing Date
KR1020210101510A KR20210105849A (en) 2019-12-16 2021-08-02 Yellow soil fermentation strain composition for water purification and water purification method using the same

Country Status (1)

Country Link
KR (2) KR20200120481A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112877267A (en) * 2021-04-21 2021-06-01 山东省淡水渔业研究院(山东省淡水渔业监测中心) Tropical bacillus strain and application thereof
CN113617829A (en) * 2021-08-01 2021-11-09 重庆工商大学 Biological oil removal method for soil containing heavy metals and waste engine oil

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101105408B1 (en) 2010-05-24 2012-01-17 한국파워트레인 주식회사 stator assembly for 3-phase motor

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101105408B1 (en) 2010-05-24 2012-01-17 한국파워트레인 주식회사 stator assembly for 3-phase motor

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112877267A (en) * 2021-04-21 2021-06-01 山东省淡水渔业研究院(山东省淡水渔业监测中心) Tropical bacillus strain and application thereof
CN113617829A (en) * 2021-08-01 2021-11-09 重庆工商大学 Biological oil removal method for soil containing heavy metals and waste engine oil

Also Published As

Publication number Publication date
KR20210105849A (en) 2021-08-27

Similar Documents

Publication Publication Date Title
CN101508505B (en) Method for removing blue algae in water and reducing algae stench
Sen et al. Relationship of algae to water pollution and waste water treatment
Ahmad et al. Comparative phycoremediation of sewage water by various species of algae
CN109678246B (en) Method suitable for treating water bloom in lakes and reservoirs and slow flow type riverways
CN104694443A (en) Improved biological microbial agent for disposing industrial sewage and preparation method and application thereof
KR20210105849A (en) Yellow soil fermentation strain composition for water purification and water purification method using the same
CN105753272A (en) Sewage treatment method for garden planning
CN110563279B (en) System and method for repairing water bodies in rivers and lakes in floating type water purification field
CN101701197B (en) Novel microorganism flora mixture and mixed nutrient medium thereof
CN107099483B (en) Composite biological agent and application thereof in treatment of mercury-containing wastewater
CN107285482B (en) Environment-friendly enzyme for purifying eutrophic water and preparation method thereof
CN105800883A (en) Microbial preparation for urban green land sewage treatment and using method thereof
CN110776215B (en) Novel method for treating black and odorous water body by side filtration assisted and enhanced microorganism in-situ remediation
KR20050020441A (en) Method and system for purifying acid mine drainage using sulfate reducing bacteria
CN105923900A (en) Sewage treatment method used in the urban green space planning
CA2641482A1 (en) Mixed bacterial culture for atrazine degradation
CN105967464A (en) Method for removing chrome-contained wastewater pollutants
US20030201224A1 (en) Microbial consortium for the biodegradation of dithiocarbamates
CN109879446A (en) It is a kind of for repairing the optimization method in polluted by nitrogen river
CN109626732B (en) Upper-mixing and lower-dropping black and odorous water body treatment method
CN110586605A (en) Stabilization treatment method for sulfur waste ore based on facultative sulfate reduction mycoderm coating
KR100217222B1 (en) Process for producing microorganisms for wastewater treatment
KR100567018B1 (en) Method for Purifying Water Pollutant Using Plant
Li et al. Flocculant and adsorbent assist submerged macrophyte colonization for the in situ repair of eutrophic water
SU1068398A1 (en) Process for biochemical purifacation of effluents from tertiary butanol

Legal Events

Date Code Title Description
E902 Notification of reason for refusal
E601 Decision to refuse application