In order to get as ecological basic data for river management, We estimated health condition of Geum-river mainstream and Mihocheon using vegetation and investigated it for phytosociologic methods. Then, collected data was analysed. Appeared plants in study area were 268 species and the number of appeared plant colonies was 54. Riparian vegetation index(RVI), vegetation health condition assessment method, was evaluated as 38.3 ‘Normal(C)’. Geum-river mainstream's upper stream1(G-U1), upper stream4(G-U4) and mid stream3(G-M3) were highest as 66.7 and Geum-river mainstream's down stream1(G-D1) was lowest by 3.3.Riparian vegetation index under upper stream, middle stream, down stream in Geum-river mainstream and Mihocheon was highest in Geum-river mainstream's upper stream and lowest in Geum--river mainstream's down stream. Riparian vegetation index was negatively correlated with biological oxygen demand(BOD) and chlorophyll-a(Chl-a) in study sites.PCA using species cover degree data of belt transect in each study sites was separated by two groups. One group was consisted of ‘best(A grade)’ and ‘good(B grade)’, the other group was comprised of ’normal(C grade)‘ and ’bad(D grade)’. Cluster analysis was separated by 5 groups: Digitaria ciliaris Koel. community group, Salix gracilistyla Miq. community group, Erigeron annuus Pers. community group, Humulus japonicus Siebold & Zucc., Salix koreensis Andersson, Miscanthus sacchariflorus Benth., and Phragmites japonica Steud. community group, Conyza canadensis Cronquist and Echinochloa crusgalli var. echinata Honda community group. Study sites having similar health condition also was grouped in analysis. These result was similar in PCA. Dominance value of study sites was significantly correlated with vegetation area, structure area, waterway area, spot width, waterway width, bank height and number of species in CCA analysis. As a result, it means that the high health condition sites are dominated by Salix, Fraxinus and phragmites spp. increasing plant diversity and the low health condition sites have a wide structure area simplifing plant diversity by river maintenance work. Thus, the hight health condition area needs to maintain condition through continuous monitoring and the low health condition area needs to restore ecosystem services.