• 한국환경복원기술학회지
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• 제17권5호
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• pp.65-77
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• 2014

The ecosystem of Jaemin stream, flowing into the center of Gongju-si, had been damaged by low water quality and lack of water quantity of the steam. However, after applying the SSB (Sustainable Structured wetland Biotop) system to the flood plain and the upstream of Jaemin stream, the efficiency of ecological water purification and ecological restoration are as follows. Through the constant maintenance and monitoring from year 2009 to year 2013 after restorative design and construction the average influent concentration of BOD5 was 4.2 mg/L, and the average effluent concentration was 1.8 mg/L, reaching ecological water purification rate of 57%. As for the T-N, the average influent concentration was 9.983 mg/L, and the average effluent concentration was 6.303 mg/L, showing the rate of 37%. For the T-P, the average influent concentration was 0.198 mg/L, and the average effluent concentration was 0.098 mg/L, being the rate of 51%. The vegetation of Jaemin stream monitored for 2 years after the restoration was composed of 51 species in 28 families which show high ratio of planted native species. As for the animals in the site, 5 species in 3 families of reptiles and amphibians, 34 species of 23 families of birds, and 3 species in 2 families of mammals were monitored, indicating that the bio-diversity of the site has improved, as well.

• 한국환경복원기술학회지
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• 제16권1호
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• pp.181-191
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• 2013

The design process of ecological and environmental detention system located in the housing district of Sinjeong 3-jigu in Seoul are as follows. At stage one, a new dispersal detention was created in the neighborhood park located near the originally planned detention. From this, the amount of storage of this dispersal detention system was enlarged from $28,337m^3/d$, the initial storage amount, to $33,606m^3/d$ as the post storage amount, responsible to the amount of rainfall which happens every 100 years. In particular, the SSB (Sustainable Structured wetland Biotop) system, which was the New Excellent Technology verified by the Ministry of Environment (No. 258) was applied to enhance ecological functioning and water quality with the detention as a constructed wetland. At stage two, the treatment plans for non-point pollutant source occurred at the initial period of rain, flowing into the detention system were built for purifying the water of the retention pond at the base of the detentions, and the water-circulation system was designed at the dispersal detentions on the period of regular rainfalls. The non-point pollutant source flowing into detention site was calculated as $11,699m^3/d$ flowing down from seven small watersheds, which occurred at the initial period of rain. In particular the SSB systems improved the average efficiency of the water processing performance to BOD 60%, SS 90%, T-N 30%, T-P 60%. At stage three, the ecological network and biological diversity were strongly considered so that it brought the residents with amenity places. In particular, the dispersal detentions were successfully designed to restore the ecological habitat of endangered plant and animal species such as narrow-mouthed.

• 한국환경복원기술학회지
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• 제13권3호
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• pp.23-35
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• 2010

A Sustainable Structured wetland Biotop (SSB) system was constructed on the floodplain of Kyungan stream in December, 2006. It purifies polluted water of Keumeo stream which flows into the stream. Water were sampled once a month at inlet and outlet from December, 2007 to December, 2008. $BOD_5$, SS, T-N and T-P were analyzed. Plant and fish species of the system were monitored twice during the period. Average influent and effluent BOD5 concentration was 6.2 and 2.2 mg/L, respectively and BOD5 removal was 50.8%. SS concentration of influent and effluent was averaged 10.1mg/L and 1.5mg/L, respectively and SS abatement amounted to 77.0%. Average influent and effluent T-N concentration was 4.9mg/L and 2.9 mg/L, respectively and T-N retention was 50.8%. T-P concentration of influent and effluent was averaged 0.386mg/L and 0.107mg/L, respectively and T-P removal amounted to 77.0%. Twenty two plant species were naturally introduced into the system, however, they didn't make up a significant portion of the plant populations compared with the planted species. Dominant plant species were in the following order; Phragmites communis > Typha latifolia > Iris pseudoacorus > Persicaria thunbergii. Five families and 15 species of fish were observed in the system including Chinese minnow (Moroco oxycephalus) which inhabits in clean water. Six more fish species were monitored in the system compared with ones living in Kyungan stream. Amphibia and reptiles accounted for 11 species of 4 orders and 7 families including Korean Salamander (Hynobius leechi) which also lives in cleanwater.

• 한국환경복원기술학회지
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• 제13권6호
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• pp.145-159
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• 2010

A Sustainable Structured wetland Biotop (SSB) system was planned, designed, and finally constructed, and maintained in the An-teo Reservoir ecological park, which is the habitat of the endangered Gold-spotted Pond Frog. The system purifies polluted water of An-teo Reservoir which flows from up to bottom within the system. Water was sampled once a month at the inlet and at the outlet from December, 2009 to August, 2010. BOD5, SS, T-N and T-P were analyzed. Average influent and effluent BOD5 concentration was 2.9 and 1.0 mg/L, respectively, and BOD5 removal was 67%. SS concentration of influent and effluent averaged 18.1 mg/L and 2.5 mg/L, respectively, and SS abatement amounted to 86%. Average influent and effluent T-N concentration was 0.426 mg/L and 0.147 mg/L, respectively, and T-N retention was 66%. T-P concentration of influent and effluent averaged 0.071 mg/L and 0.022 mg/L, respectively, and T-P removal amounted to 68%. Plant and frog species of the system were monitored during the period. Amphibia and reptiles provided 7 species and 4 families including the Endangered Gold-Spotted Pond Frog (Rana chosenica ) which also lives in the system. Twenty-six plant species were naturally introduced into the system, however, they didn't make up a significant portion of the plant populations compared with the planted species. The endangered plants, Bladderwort (Utricularia vulgaris var. japonica ) and Euryale ferox were observed in An-teo Reservoir as well as in the system.

• 한국습지학회지
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• 제21권4호
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• pp.374-383
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• 2019

왕포천은 충청남도 부여군에 위치하고 있는 하천으로 유로 연장이 길지 않고, 경작지 및 취락지를 통과하는 하천으로 수질이 불량하고, 수량이 부족한 하천이다. 따라서 부여 하수처리수와 왕포천의 비점오염원 1,500~7,000 ㎥/d를 처리 하고 생태계를 복원하고자 SSB (Sustainable Structured wetland Biotop) system의 처리습지를 적용한 결과는 다음과 같다. 왕포천 복원에 대한 설계 및 시공 완료후인 2016년부터 2018년까지 지속적인 관리와 모니터링을 실시한 결과 BOD₅ 평균 농도는 7.3 mg/L, 평균 유출농도는 2.1 mg/L로 71.2%의 개선 효율을 나타내었다. T-N은 평균 유입 농도가 7.953 mg/L, 평균 유출 농도가 3.379 mg/L로 57.5 %, T-P의 평균 유입 농도는 0.177 mg/L, 평균 유출 농도는 0.052 mg/L로 70.7 %의 개선효과를 나타냈다. 왕포천 수질정화시설을 통한 생태계복원에 대한 모니터링 결과는 복원 후 3년 동안 모니터링 된 왕포천 수질정화시스템의 식물상은 21과 41종으로 식재수종보다 자연유입된 식물종의 비율이 높게 나타났다. 동물상에 대한 모니터링 결과, 양서류와 파충류는 3과 6종, 조류는 15과 25종, 포유류는 5과 5종이 왕포천과 생태적수질정화시설을 이동하며 서식하는 것으로 확인되어, 생물다양성도 창출및 향상된 것으로 나타났다.

• 환경영향평가
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• 제26권6호
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• pp.508-523
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• 2017

본 연구는 매노천 생태하천복원을 위한 생태적수질정화비오톱 시스템과 생태어도(Fish-way) 등의 적용 대상지를 중심으로 생태하천 복원 전 후를 모니터링하였다. 어류는 복원전 서식이 확인되지 않았던 생태적수질정화비오톱 습지에서 총 11종 191개체가 창출복원된 것으로 조사되었다. 특히 복원목표종인 돌마자와 참종개가 생태적수질정화비오톱 습지에서 서식함이 모니터링되어, 미소서식처와 건전한 Fish-way가 창출되었음을 확인할 수 있었다. 양서류는 복원후 활동성이 높은 3차 조사시기에 습지와 그 주변에서 다수의 참개구리 서식으로 복원되었음이 확인되었다. 포유류는 수달이 습지와 Fish-way를 서식영역으로 활용하는 것이 확인되어 환경부 멸종위기 제1급이자 천연기념물인 수달 서식지가 복원된 것으로 조사되었다. 식물상의 경우 조사지역에 출현하는 관속식물은 복원 전 총 7과 13종, 복원직후 15과 19종, 복원후 총 22과 33종으로 증가되었다. 복원후 식생은 달뿌리풀 군락 등의 다양한 생태계의 기초생산자이자 수질정화에 기여하는 식재종인 정수식물군락이 형성된 것으로 조사되었다. 수질 모니터링 결과, 평균적으로 BOD 64.3%, T-N 47.2%, T-P 80.7%의 처리효율을 나타내었다. 생태계를 교란하는 제한요인(limiting factor)이 되는 비점오염원이 성공적으로 처리됨으로써 I, II등급수질에 서식하는 목표종이 창출적으로 복원되었다.

• 한국환경복원기술학회지
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• 제9권3호
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• pp.1-16
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• 2006

The purpose of this study is to develop design model of ecological park as stormwater storage facilities. The results are as follows : First, the design model of ecological park as stormwater storage facilities consider ecological and landscape characteristics such as high efficiency of land use, function as disaster prevention, ecological water purification, formation of habitat for flora and fauna. Second, this study demonstrates two types of plane structure and eight types of designed section. They can be combined and designed depending on conditions of each site. The facilities of stormwater storage conduct disaster prevention system and ecological park. Retention pond in stormwater storage facilities for ecological park also should be made for ecological restoration in the site. Third, the ecological park provide the basis for ecological network from in-site to out-site. Therefore its conservation and restoration plan consider the ecosystems of the site. Fourth, the most important factor for maintenance and management for retention pond is keeping water quality. Sustainable Structured wetland Biotop system is suggested for ecological water purification system in the retention pond which is one of the constructed wetland system using multi-celled aquatic plant and pond. This system can also provide habitat for animals and plants, water friendly park for men, and beautiful landscape.