발생부하원단위와 수치표고모형을 이용한 하천유역 오염부하량 산정

양홍모,김혁,Yang, Hong-Mo,Kim, Hyuk 한국조경학회 2001 韓國造景學會誌 Vol.29 No.1

The purpose of this study is to compare calculated pollutant loadings using pollutant load unit factors and vector type coverage, and expected mean concentration(EMC) and raster type of digital elevation model(DEM). This study is also focusing on comparison of the advantages and the disadvantages of the two methods, and seeking for a method of calculation of pollutant loadings using DEM. Estimation of pollutant inputs using pollutant load unit factors has limitations in identifying seasonal variations of pollutant loadings. Seasonal changes of runoffs should be considered in the calculation of pollutant loadings from catchments into reservoirs. Evaluation of pollutant inputs using runoff-coefficient and EMC can overcome these drawbacks. Proper EMC and runoff-coefficient values for the Koeup stream catchments of the Koheung estuarine lake were drawn from review of related papers. Arc/Info was employed to establish database of spatial and attribute data of point and non-point pollutant sources and characteristics of the catchments. ArcView was used to calculate point and non-point pollutant loadings. Pollutant loads estimated with either unit factors-coverages, i.e., pollutant load unit factors and vector coverages f point sources and land use, or EMC and digital elevation mode(DEM) were compared with stream monitoring loads. We have found that some differences were shown between monitoring results and estimated loads by Unit Factors-Coverage and EMC-DEM. Monthly variations of pollutant loads evaluated with EMC-DEM were similar to those with monitoring result. The method using EMC-DEM can calculate accumulated flows and pollutant loads and can be utilized to identify stream networks. A future research on correcting the difference between vector type stream using flow direction grid and digitalizing vector type should be conducted in order to obtain more exact calculation of pollutant loadings.

도시하천 제방사면에 식재한 몇몇 벼과식물의 활착 및 군락유지 특성

양홍모,Yang, Hong-Mo 한국조경학회 2017 韓國造景學會誌 Vol.45 No.5

도시하천 제방사면의 벼과식물 활착과 군락형성 연구를 위해 2010년 10월 중순 물억새, 억새, 띠, 새를 줄떼식재하였다. 플라스틱 묘상(길이 60cm ${\times}$ 너비 30cm ${\times}$ 깊이 5cm)에 원예용상토를 4cm 깊이로 채우고 실험초종의 씨앗을 2010년 4월 하순 파종한 후 2010년 10월 초까지 형성된 뗏장을 너비 6cm ${\times}$ 길이 15cm ${\times}$ 두께 4cm로 잘라서 제방사면에 수평 폭 약 10~15cm 간격으로 심었다. 줄떼식재 후 군락형성을 유도하기 위해 2011년~2013년까지 3년간 매년 2회 잡초를 제거하였다. 실험초종 모두 2012년에 줄떼 간격의 빈 공간을 줄기가 상당부분 채워 초기군락이 형성되었으며, 2013년에는 줄떼 간격의 빈 공간을 거의 채워 군락이 형성되었다. 군락형성 후 2014년과 2015년은 잡초제거 없이 군락유지가 가능한지 관찰하였다. 2013년과 2014년의 줄기수간, 초장간 t-검정과, 2014년과 2015년의 줄기수간, 초장간 t-검정을 수행하였다. t-검정에는 5월, 7월, 9월에 조사한 줄기수와 초장을 활용하였다. 실험초종 모두 2014년의 줄기수와 초장이 2013년보다 줄어들어(p<0.001) 잡초의 피해를 입었다. 물억새, 억새, 띠는 2014년과 2015년의 줄기수와 초장에 차이가 없어(p>0.05) 군락형성 후 잡초제거 없이 군락이 유지되었으나, 새는 2015년의 줄기수와 초장이 2014년보다 현저히 줄어들어(p<0.001) 잡초의 피해가 커 군락유지가 어려웠다. 하천제방사면의 초본류 군락 형성과 유지의 관점에서 줄떼식재의 경우 물억새, 억새, 띠가 적합한 초종으로 나타났다. 실험기간 5년 매년 9월에 조사한 물억새, 억새, 띠, 새의 줄떼식재와 포트식재 간 줄기수와 초장의 t-검정에서, 줄기수는 줄떼식재가 포트식재보다 많았고(p<0.001), 초장은 포트식재가 줄떼식재보다 길었다(p<0.05). 줄기수가 상대적으로 많은 줄떼식재가 제방사면 유실보호 관점에서 포트식재보다 유리한 것으로 드러났다. To investigate rooting and community forming ability, sod strips of Gramineae such as Miscanthus sacchariflorus (Maxim.) Benth., Miscanthus sinensis var. purpurascens(Andersson) Rendle, Imperata cylindrica var. koenigii(Retz.) Pilg., and Arundinella hirta(Thunb.) Tanaka were planted horizontally at a width of 10~15cm in October 2010 on the bank slope of Kwangju Stream in Korea. Seeds of each species were sown in April 2010 in plastic seedbeds(60cm length ${\times}$ 30cm width ${\times}$ 5cm depth) filled with 4cm of garden soil and grew until October 2010 to form rectangular sod, which then was cut into multiple strips(20cm length ${\times}$ 6cm width ${\times}$ 4cm root depth). Weeds growing on the experiment sites were removed twice a year until those four species had formed a community by 2013. Weeds were not eradicated during 2014 and 2015 to observe whether the community formation can be maintained without weed removal. t-tests on stem numbers and heights in May, July, and September were conducted between 2013 and 2014, and between 2014 and 2015. Stem numbers and heights of the four species in 2014 were significantly decreased(p<0.001) compared with those in 2013 due to weed damage to their growth in 2014. Stem numbers and heights of Miscanthus sacchariflorus(Maxim.) Benth., Miscanthus sinensis var. purpurascens(Andersson) Rendle, Imperata cylindrica var. koenigii(Retz.) Pilg. in 2015 were similar to those in 2014(p>0.05). Stem numbers and heights of Arundinella hirta(Thunb.) Tanaka in 2015, however, were significantly reduced compared with those in 2014(p<0.001) due to weed impact on its growth. After three years of weed removal, a community of each species was formed. Miscanthus sacchariflorus(Maxim.) Benth., Miscanthus sinensis var. purpurascens(Andersson) Rendle, Imperata cylindrica var. koenigii(Retz.) Pilg. were able to establish communities without any further weed removal. Arundinella hirta(Thunb.) Tanaka, however, was not able to maintain its community due to considerable damage to its growth caused by weeds even after three years of weed removal. Miscanthus sacchariflorus(Maxim.) Benth., Miscanthus sinensis var. purpurascens(Andersson) Rendle, Imperata cylindrica var. koenigii(Retz.) Pilg. are more suitable to sod strip plantings on stream bank slopes in terms of the maintenance of community formation without weed eradication. t-test on stem numbers and heights each September during the five year experiment period between sod strip planting and potted plants of the four species were conducted. Stem numbers of strip sod plantings were significantly higher(p<0.001) than those of potted one. Heights of strip sod plantings, however, were significantly lower(p<0.05) than those of the potted samples. Therefore, strip sod planting is more advantageous regarding bank slope erosion protection due to the higher number of stems.

광주천 고수부지에 조성한 자유수면인공습지의 인 제거

양홍모,Yang, Hong-Mo 한국조경학회 2012 韓國造景學會誌 Vol.40 No.1

하천수를 정화하는 자유수면인공습지의 정수식물 성장기(4~9월)와 비성장기(1~3월과 10~12월)의 $PO_4-P$와 TP제거율을 비교 연구하였다. 실험 습지 시스템은 광주광역시를 흐르는 광주천 중류 고수부지에 2008년 조성되었으며, 길이 46m, 폭 5m 규모이다. 2008년 포트에서 2년 자란 부들(Typha angustifloria L.)과 줄(Zizania latifolia Turcz)을 시스템의 1/2씩 각각 식재하였다. 광주천의 물이 자연유하로 시스템에 유입되며, 처리수는 광주천으로 방류된다. 유입수의 양과 수심은 밸브와 위어(weir)로 조절할 수 있다. 유입수 및 유출수의 인 농도를 2010년 1월부터 12월까지 7~10일 간격으로 조사 분석하였다. 하루에 약 $710m^3$의 하천수가 시스템으로 유입되어, 체류시간은 약 1.5hr이었다. 조사기간 유입수와 유출수의 $PO_4-P$ 평균농도는 각각 0.144, 0.105mg/L이었으며, $PO_4-P$ 평균제거율은 28.1%였다. 유입수와 유출수의 TP평균농도는 각각 0.144, 0.105mg/L이었으며, TP 평균제거율은 20.7%를 보였다. t 검정결과, 정수식물 성장기의 $PO_4-P$ 제거율(31.448)이 비성장기 $PO_4-P$ 제거율(25.829)보다 높았으며(p<0.001), 정수식물 성장기의 TP 제거율(27.230)도 비성장기의 TP 제거율(14.856)보다 높게(p<0.001) 나타났다. 인공습지에서 인 제거는 잔재물-토양 층의 흡착, 입자성 인과 Ca, Fe, Al과 결합된 인산염의 침전, 그리고 정수식물의 흡수가 중요하다. 정수식물 성장기가 비성장기보다 $PO_4-P$와 TP의 제거율이 상대적으로 높은 원인은 흡착과 침전에 의한 인 제거는 계절에 관계없이 일어나나, 정수식물의 흡수는 성수식물 성장기에만 일어나기 때문이다. Removal rates of $PO_4-P$ and TP in a free water surface wetland system were investigated. The system was established in 2008 on a floodplain in the middle reach of the Gwangju Stream flowing through Gwangju City. Its dimensions were 46 meters in length and 5 meters in width. Two year old Typha angustifloria L. growing in pots were planted on half of the area and Zizania latifolia Turcz on the other half in 2008. Stream water was funneled into the wetlands by gravity flow, and its effluent was discharged back into the stream. The influent volume was controlled by valves and water depth was adjusted by wires. Volume and water quality of inflow and outflow were analyzed from January to December in 2010. Inflow into the system averaged approximately $710m^3/day$ and hydraulic residence time was about 1.5 hours. Average influent and effluent $PO_4-P$ concentration were 0.144 and 0.103mg/L, respectively, and $PO_4-P$ abatement amounted to 28.6%. Influent and effluent TP concentration averaged 0.333 and 0.262mg/L, respectively, and TP retention reached to 20.7%.$PO_4-P$ removal rate(%) during plant growing season(31.448) was significantly high(p<0.001) when compared with that during plant non-growing season(25.829). TP abatement rate(%) during plant growing season(27.230) was also significantly high(p<0.001) when compared with that of the non-growing season(14.856). Major phosphorous removals in the system resulted from adsorption of phosphorous in the litter-soil layers; sedimentation of particulate phosphorous and Ca, Al, Fe bounded phosphates; and absorption of phosphorous by emergent plants. The adsorption and sedimentation occurred throughout the year, however, the absorption took place during plant growing season. This resulted in higher removals of $PO_4-P$ and TP during plant growing season.

도시하천 제방사면에 식재한 다년생 초본류의 군락 형성 비교

양홍모,Yang, Hong-Mo 한국조경학회 2014 韓國造景學會誌 Vol.42 No.1

도시하천 제방사면의 다년생 초본류 군락 형성 연구를 위해 2009년 4월 중순 물억새, 억새, 띠, 수크령, 새를 식재하였다. 새는 분주를 식재하였고, 나머지 초종은 이년생 포트를 식재하였다. 식재 후 3년간 매년 2회의 잡초 제거를 통해 2011년 군락이 형성되었다. 2012년과 2013년은 잡초를 제거하지 않고 실험초종이 군락을 유지하는지 관찰하였다. 잡초를 제거한 2011년과 잡초를 제거하지 않은 2012년간, 잡초를 제거하지 않은 2012년과 2013년간 줄기수와 초장에 차이가 있는지 5월, 7월 9월의 줄기수와 초장을 활용하여 유의수준 0.05에서 t-검정을 하였다. 실험초종 모두 2012년의 줄기수가 2011년보다 적어(p<0.001) 잡초의 피해를 입었다. 억새, 띠, 수크령, 새의 초장은 2012년이 2011년보다 작아 잡초의 피해가 나타났다. 물억새의 초장은 5월과 7월에 차이를 보여 잡초의 피해를 입었으나 (p<0.001), 9월에는 차이가 없어(p=0.098) 피해를 입지 않았다. 2012년과 2013년간t-검정 결과, 새를 제외한 나머지 초종은 줄기수와 초장에 차이가 없었다(p>0.05). 이들 초종은 군락이 형성된 후 잡초의 피해 없이 군락이 유지되었다. 새는 줄기수와 초장 모두 차이를 보여 잡초의 피해가 컸다. 물억새, 억새, 띠, 수크령은 군락 형성 후 잡초 제거 없이 군락이 유지되었으나, 새는 잡초의 피해가 커 군락 유지가 어려웠다. 군락 형성 및 유지, 하천경관 개선, 제방사면 보호의 관점에서 물억새, 억새, 띠가 적합한 것으로 나타났다. In order to investigate community formation ability, herbaceous perennials such as Miscanthus sacchariflorus Bentham, Miscanthus sinensis var. purpurascens Rendle, Imperata cylindrica Linne, Pennisetum alopecuroides (L.) Spreng. and Arundinella hirta Tanaka were planted in April 2009 at the levee slope of Gwangju Stream in South Korea. Miscanthus sacchariflorus Bentham, Miscanthus sinensis var. purpurascens Rendle, Imperata cylindrica Linne and Pennisetum alopecuroides (L.) Spreng. which grew in pots for two years and divided rhizomes of Arundinella hirta Tanaka gathered from fields were employed. Weeds growing on the experiment sites were removed twice a year until 2011 when the plant species were formed into community. Weeds were not eradicated during 2012 and 2013 to observe community sustainability of the species. T-tests on stem numbers and heights in May, July and September were conducted between 2011 and 2012, and between 2012 and 2013. Stem numbers of the five species in 2012 were significantly reduced(p<0.001) compared with those in 2011, which were attributed to weed growth in 2012. Heights of Miscanthus sinensis var. purpurascens Rendle, Imperata cylindrica Linne, Pennisetum alopecuroides (L.) Spreng. and Arundinella hirta Tanaka in 2012 were significantly lower than those in 2011(p<0.001), which resulted from weed invasion. Heights of Miscanthus sacchariflorus Bentham in May and July 2012 were significantly decreased compared with those in 2011(p<0.001), however, heights of Miscanthus sacchariflorus Bentham in September 2012 were almost the same as those in 2011(p>0.05). Miscanthus sacchariflorus Bentham was able to compete against weeds in September 2012. Stem numbers and heights of Miscanthus sacchariflorus Bentham, Miscanthus sinensis var. purpurascens Rendle, Imperata cylindrica Linne and Pennisetum alopecuroides (L.) Spreng. in 2013 were similar to those in 2012(p>0.05). However, stem numbers and heights of Arundinella hirta Tanaka in 2013 were significantly decreased compared with those in 2012(p<0.001). After community formation, Miscanthus sacchariflorus Bentham, Miscanthus sinensis var. purpurascens Rendle, Imperata cylindrica Linne and Pennisetum alopecuroides (L.) Spreng. were able to maintain its community without weed removal. However, Arundinella hirta Tanaka was unable to establish its community due to the weed growth. Miscanthus sacchariflorus Bentham, Miscanthus sinensis var. purpurascens Rendle, Imperata cylindrica Linne are more suitable to stream levee slope environment in terms of community formation and maintenance, stream landscape enhancement and slope erosion control.

신양천 하천수정화 연못시스템의 처리수준 및 연못반응

양홍모 ( Hong Mo Yang ) 한국환경복원기술학회 2005 한국환경복원기술학회지 Vol.8 No.6

하천수정화 여과습지에서 성장하는 갈대의 영양염류 흡수량

양홍모 ( Hong Mo Yang ) 한국환경복원기술학회 2006 한국환경복원기술학회지 Vol.9 No.1

자연 및 인간 환경이 공존하는 지역의 환경계획에 있어 생태계모형 접근

梁弘模(Yang Hong-Mo) 대한국토·도시계획학회 1997 國土計劃 Vol.32 No.4

하천수를 정화하는 갈대습지의 개수부에 의한 질소제거 비교

양홍모 ( Hong Mo Yang ) 한국환경복원기술학회 2005 한국환경복원기술학회지 Vol.8 No.1

분뇨처리장 방류수정화 갈대습지셀의 초기 운영단계 질산성질소 제거

양홍모 ( Hong Mo Yang ) 한국환경복원기술학회 2004 한국환경복원기술학회지 Vol.7 No.5

GIS를 응용한 주암 상수원수계의 오염원 DB 구축과 수질관리 생태계모형

양홍모 ( Hong Mo Yang ),권유리 ( Yu Ri Kwon ) 한국환경생태학회 2000 한국환경생태학회지 Vol.13 No.3