Updated on 2024/02/01

写真a

 
NAGARE Hideaki
 
Organization
Faculty of Environmental, Life, Natural Science and Technology Professor
Position
Professor
External link

Degree

  • 博士(工学) ( 京都大学 )

Research Interests

  • water quality

  • water environment

  • environmental engineering

  • wastewater treatment

Research Areas

  • Environmental Science/Agriculture Science / Environmental load reduction and remediation

  • Environmental Science/Agriculture Science / Environmental dynamic analysis

  • Social Infrastructure (Civil Engineering, Architecture, Disaster Prevention) / Environmental systems for civil engineering

Education

  • Kyoto University   大学院工学研究科   環境工学専攻

    1998.4 - 2001.3

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    Country: Japan

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  • Hokkaido University   大学院工学研究科   衛生工学専攻

    1991.4 - 1993.3

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    Country: Japan

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  • Hokkaido University   工学部   衛生工学科

    1987.4 - 1991.3

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    Country: Japan

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Research History

  • Okayama University   Faculty of Environmental, Life, Natural Science and Technology   Professor

    2023.4

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    Country:Japan

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  • Okayama University   The Graduate School of Environmental and Life Science   Professor

    2021.4 - 2023.3

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    Country:Japan

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  • Okayama University   The Graduate School of Environmental and Life Science   Associate Professor

    2018.4 - 2021.3

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    Country:Japan

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  • Okayama University   Environmental Management Center   Associate Professor

    2016.4 - 2018.3

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    Country:Japan

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  • Okayama University   The Graduate School of Environmental and Life Science   Associate Professor

    2012.4 - 2016.3

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    Country:Japan

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  • Okayama University   Graduate School of Environmental Science   Associate Professor

    2010.4 - 2012.3

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    Country:Japan

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  • Kitami Institute of Technology   Faculty of Engineering   Associate Professor

    2007.4 - 2010.3

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    Country:Japan

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  • Kyoto University   Graduate School of Engineering   Lecturer

    2003.10 - 2007.3

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    Country:Japan

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  • Kyoto University   Graduate School of Engineering   Assistant Professor

    2002.10 - 2003.9

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    Country:Japan

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  • Kyoto University   Graduate School of Engineering   Postdoctoral researcher

    2001.4 - 2002.9

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    Country:Japan

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  • Hitachi, Ltd.,

    1993.4 - 1998.3

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    Country:Japan

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Professional Memberships

Committee Memberships

  • 日本水環境学会   セミナー企画部会委員  

    2019.7 - 2023.6   

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    Committee type:Academic society

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  • 土木学会   環境工学委員会委員兼幹事  

    2019.4 - 2021.3   

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    Committee type:Academic society

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  • 土木学会   環境工学委員会論文集小委員会委員  

    2019.4 - 2021.3   

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    Committee type:Academic society

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  • 国土交通省   小田川合流点付替え事業掘削土対策検討会委員  

    2018.3 - 2019.3   

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    Committee type:Government

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  • 岡山市   環境総合審議会委員  

    2017.4 - 2021.3   

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    Committee type:Municipal

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  • 瀬戸内市   福山浄水場施設更新整備事業 事業者選定審査委員  

    2016.5 - 2017.5   

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    Committee type:Municipal

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  • 土木学会   環境賞選考委員会委員  

    2015.7 - 2017.6   

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    Committee type:Academic society

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  • 日本水環境学会   編集企画部会委員  

    2013.7 - 2016.6   

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    Committee type:Academic society

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  • 土木学会   環境工学委員会委員  

    2013.4 - 2017.3   

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    Committee type:Academic society

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  • 備前市   総合評価方式一般競争入札における学識経験者  

    2013.1 - 2014.6   

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    Committee type:Municipal

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  • 土木学会   中国支部幹事  

    2012.4 - 2013.3   

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    Committee type:Academic society

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  • 岡山市   公害対策審議会委員  

    2011.8 - 2017.3   

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    Committee type:Municipal

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  • 日本水環境学会   中国・四国支部幹事  

    2011.4   

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  • 岡山市   水道事業審議会委員  

    2011.4 - 2013.3   

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    Committee type:Municipal

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  • 岡山市   環境保全審査会専門委員  

    2010.11 - 2012.8   

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    Committee type:Municipal

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  • 岡山県   大谷川ダム検討会議委員  

    2010.11 - 2011.7   

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    Committee type:Municipal

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  • 北海道   網走支庁産業振興部総合評価審査委員会  

    2009.5 - 2011.3   

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    Committee type:Municipal

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  • 北海道   網走西部森づくり総合評価審査委員会委員  

    2009.5 - 2011.3   

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    Committee type:Municipal

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  • 北海道   網走東部森づくり総合評価審査委員会  

    2009.5 - 2011.3   

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    Committee type:Municipal

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  • 北海道   網走土木現業所総合評価審査委員会  

    2009.5 - 2011.3   

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    Committee type:Municipal

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  • 土木学会   環境工学委員会委員  

    2009.4 - 2010.3   

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    Committee type:Academic society

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  • 日本水環境学会   北海道支部幹事  

    2009.4 - 2010.3   

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  • 北見市   上下水道審議会委員  

    2009.1 - 2010.8   

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    Committee type:Municipal

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  • 水文・水資源学会   編集出版委員会委員  

    2008.4 - 2010.3   

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  • (財) 北海道河川防災研究センター   平成19年常呂川の濁水に関する流域対策検討会 委員  

    2007.8 - 2008.3   

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    Committee type:Other

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  • 北見市   水道水の断水に関する原因技術調査委員会委員  

    2007.7 - 2007.8   

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    Committee type:Municipal

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  • (財) 下水道新技術推進機構   再生水を活用した都市の水環境改善検討委員会委員  

    2005.8 - 2006.3   

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    Committee type:Other

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  • 滋賀県   水環境監視のあり方検討会 委員  

    2004.10 - 2005.3   

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Papers

  • Identification of cell type of microalga Haematococcus lacustris by image recognition Reviewed

    Nagare, H, Masuda, T, Ishikawa, C

    Japanese Journal of JSCE   79 ( 25 )   23-25047   2023.11

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    Authorship:Lead author   Language:Japanese   Publishing type:Research paper (scientific journal)  

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  • Characterization of Effluent Water Quality from Hydroponic Cultivation System Reviewed

    Hideaki Nagare, Youhei Nomura, Kenta Nakanishi, Satoshi Akao, Taku Fujiwara

    Journal of Water and Environment Technology   19 ( 2 )   64 - 73   2021

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    Authorship:Lead author   Language:English   Publishing type:Research paper (scientific journal)   Publisher:Japan Society on Water Environment  

    DOI: 10.2965/jwet.20-096

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  • Simultaneous recovery of phosphorus and potassium from biomass as magnesium salt Reviewed

    Hideaki NAGARE, Takumi IWATA, Ayako EBI, Satoshi AKAO, Morihiro MAEDA, Daisuke YASUTAKE, Taku FUJIWARA

    Journal of Japan Society of Civil Engineers, Ser. G (Environmental Research)   76 ( 7 )   III_181 - III_187   2020

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    Authorship:Lead author   Language:English   Publishing type:Research paper (scientific journal)   Publisher:Japan Society of Civil Engineers  

    DOI: 10.2208/jscejer.76.7_iii_181

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  • Effects of cultivation period on catch crop chemical composition and potential for bioenergy production Reviewed

    S. Akao, D. Yasutake, K. Kondo, H. Nagare, M. Maeda, T. Fujiwara

    Industrial Crops and Products   111   787 - 793   2018.1

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:Elsevier B.V.  

    The first step in biofuel and/or bio-based bulk chemical material production is assessing the amounts of useful substances in a potential biomass. Sugar, nutrients, ash, and functional ingredients (such as antioxidant compounds) in premature dent corn biomass cultivated as a catch crop (plant density
    60 shoots m−2) over different cultivation periods (29 days, 49 days, 83 days) were investigated. The sugar recovery amount was estimated by multiplying two regression curves (saccharification efficiency curve, quadratic regression curve
    dry weight growth curve, Gompertz curve). A simple economic analysis for ethanol production from the catch crop biomass was also carried out using previously reported process costs and the estimated sugar recovery amount. High plant density led to accumulation of plant biomass providing high amounts of plant dry weight and derived sugars per unit area. About 2700 g DW m−2 (about 1400 g sugar m−2) was harvested in the 49-day cultivation. The amount is significant compared with biomass yields of other candidates for energy crops. The estimated sugar recovery amount reached its maximum value near the end of experimental period (79-day cultivation). The longer cultivation period was better for sugar recovery although there was a slight decrease in saccharification efficiency with cultivation time. Based on the economic analysis, a higher ethanol price (about 200% higher than the current wholesale price) would be required for catch crop financial independence with around 50-day cultivation. Production of ethanol from catch crop biomass would not be feasible in the current situation. However, condensed biomass production through catch crops is still attractive and requires further research.

    DOI: 10.1016/j.indcrop.2017.11.039

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  • 農産業における水・バイオマス循環利用に関する最新研究動向

    藤原拓, 永禮英明, 山田正人, 和木美代子, 前田守弘, 日髙平, 今井剛, 井原一高, 井上大介

    水環境学会誌   40 ( 12 )   416 - 423   2017

  • Non-sterile simultaneous saccharification and fermentation of corn leaves and stalks to l-lactic acid without external nutrient addition Reviewed

    Satoshi Akao, Hideaki Nagare, Morihiro Maeda, Keisuke Kondo, Taku Fujiwara

    JOURNAL OF MATERIAL CYCLES AND WASTE MANAGEMENT   18 ( 2 )   208 - 214   2016.4

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:SPRINGER  

    Fermentation of lignocellulosic biomass requires auxiliary materials, including nutrients, to ensure the proliferation of microorganisms. Nutrients are usually inexpensive, but their contribution to the cost is considerable because of the very low prices of fermentation products, such as bio-ethanol. Using substances present in native lignocellulosic biomass as nutrients for fermentation was proposed and demonstrated. Leaves and stalks of corn plants were used as biomass, and nutrients were recovered as a nutrient solution by soaking them in water before alkaline peroxide pretreatment. Pretreated biomass and the nutrient solution derived from the same lot were used for non-sterile simultaneous enzymatic saccharification and thermophilic l-lactic acid fermentation (SSF). Using the nutrient solution in the saccharification step did not impact sugar recovery, and instead improved sugar yields because of the presence of eluted sugars in the solution. The l-lactic acid yield of 0.33 g g(-1) based on native biomass weight indicated that the nutrient solution functioned as a source of nutrients and sugars, especially as a source of essential phosphorus. Comparatively, autoclaved SSF yielded less or no l-lactic acid, indicating an apparent inhibitive effect derived from the nutrient solution on bacterial growth.

    DOI: 10.1007/s10163-015-0390-y

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  • Simulation of the Collection of Catch Crops for the Recovery of Agricultural Resources using Geographic and Statistical Data Reviewed

    Masayuki Matsuoka, Hideaki Nagare, Taku Fujiwara

    TRANSACTIONS IN GIS   20 ( 2 )   221 - 239   2016.4

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:WILEY-BLACKWELL  

    The cultivation of catch crops has great potential in agricultural areas for the recovery of nutrients, mitigation of groundwater contamination, and secondary utilization of harvestry. To estimate the potential volume of catch crops that can be collected at prospective locations, we simulated the cultivation and collection process at a regional scale using geographic and statistical data. Three types of geographic data, namely the locations of greenhouses, collecting stations and road networks, were used in a geographic information system to compute the volume of collected catch crops and carrying distance between greenhouses and collecting stations. Carbon emission from transportation of the catch crop was calculated using an improved ton-km method, and the results were compared with the carbon content of the catch crop to evaluate the carbon balance. We found that the total fresh weight of the collected catch crops was 67900 t, of which 70% was collected at the top 15 of 73 stations. Carbon emissions from transportation ranged from >1 to 12% of the carbon content of the catch crop. The analytical method used in this study can readily be applied to other environmental studies concerning the collection of agricultural products and other biomass resources.

    DOI: 10.1111/tgis.12153

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  • Nitrous oxide emissions during biological soil disinfestation with different organic matter and plastic mulch films in laboratory-scale tests Reviewed

    Morihiro Maeda, Eisuke Kayano, Taku Fujiwara, Hideaki Nagare, Satoshi Akao

    ENVIRONMENTAL TECHNOLOGY   37 ( 4 )   432 - 438   2016.2

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:TAYLOR & FRANCIS LTD  

    Nitrous oxide (N2O), which is a greenhouse gas, may be more emitted as an intermediate product of denitrification during biological soil disinfestation. The biological soil disinfestation is a method to suppress soil-borne pathogens under reductive soil conditions produced by the application of organic matter and water irrigation with plastic film. The objective of the study was to determine the effects of different organic matter and mulch films on N2O emissions during biological soil disinfestation. Grey lowland soil amended with cattle compost plus rice bran (0.2%), rice husk (0.2%) or dent corn (0.1%, 0.2% and 0.4%) was incubated at 100% water-holding capacity with or without plastic films made of polyvinyl chloride (PVC) and triple-layer polyolefin (3PO) for 72h at 50 degrees C. Permeation of the two films was also measured at 25 degrees C and 50 degrees C. Results showed that incorporation of organic matter increased N2O emissions compared with no organic matter addition at 50 degrees C. Incorporation of rice bran and dent corn with easily decomposable C and low C:N ratios increased N2O emissions for the first 12h, but thereafter, available C supply from these amendments suppressed N2O emissions. Permeability of mulch films increased at a higher temperature and was larger for PVC than for 3PO. Our study indicated that rice husk should not be used for soil disinfestation and that application rates of organic matter must be determined based on their decomposability. Moreover, mulch film covering would not suppress N2O emission in biological soil disinfestation because of high temperature.

    DOI: 10.1080/09593330.2015.1092494

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  • Nitrous oxide and carbon dioxide emissions from paddy soil treated with rice husk products at different moisture contents in a short-term experiment Reviewed

    Ha, T.K.T, Maeda, M, Fujiwara, T, Nagare, H, Akao, S, Tran, Q. T

    Journal of Environmental Science for Sustainable Society   7   9 - 15   2016

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    Language:English   Publisher:Graduate School of Environmental and Life Science, Okayama University  

    A short-term study was conducted to investigate the effects of additions of rice husk products on nitrous oxide (N2O) and carbon dioxide (CO2) emissions from paddy soil at different soil moisture contents. Soil amended with raw rice husk (RR, 2% on a dry weight basis), rice husk char (RC, 2%), rice husk ash (RA, 2%) or no amendment (CT) was incubated at 40%, 60%, or 80% water-holding capacity (WHC) in a 100-mL bottle for 120 h. Results showed that N2O emission was lower at 40% WHC compared with other WHC treatments. At 60% and 80% WHC, N2O emissions peaked at 24 h of incubation in most treatments. The highest emission of N2O was recorded in the RR addition at 80% WHC. Additions of RC and RA decreased cumulative N2O emissions from soil at 24 h (by 24% at 60% WHC and 51% at 80% WHC for RC, and 90% at 60% WHC and 80% WHC for RA) compared with the CT treatment. Regardless of the soil moisture content, RR enhanced cumulative CO2 emission for 120 h, whereas no significant difference was detected among RC, RA and CT treatments (P > 0.05). Our short-term results indicated that application of rice husk char or ash to soil reduced N2O emission, whereas direct incorporation of rice husk into soil enhanced CO2 and N2O emissions.

    DOI: 10.3107/jesss.7.9

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  • 大型水生植物からのリン回収 Reviewed

    永禮英明, 渡辺諒, 藤原拓, 赤尾聡史, 前田守弘

    土木学会論文集G (環境)   72 ( 8 )   III_249-III_254   2016

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    DOI: 10.2208/jscejer.72.III_249

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  • Effects of soil type and nitrate concentration on denitrification products (N2O and N2) under flooded conditions in laboratory microcosms

    Thi Kim Thanh Ha, Morihiro Maeda, Taku Fujiwara, Hideaki Nagare, Satoshi Akao

    SOIL SCIENCE AND PLANT NUTRITION   61 ( 6 )   999 - 1004   2015.11

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:TAYLOR & FRANCIS LTD  

    Denitrification products nitrous oxide ((N2O) and nitrogen (N-2)) were measured in three flooded soils (paddy soil from Vietnam, PV; mangrove soil from Vietnam, MV; paddy soil from Japan, PJ) with different nitrate (NO3-) concentrations. Closed incubation experiments were conducted in 100-mL bottles for 7d at 25 degrees C. Each bottle contained 2g of air-dried soil and 25mL solution with NO3- (concentration 0, 5 or 10mgNL(-1)) with or without acetylene (C2H2). The N2O + N-2 emissions were estimated by the C2H2 inhibition method. Results showed that N2O + N-2 emissions for 7d were positively correlated with those of NO3- removal from solution with C2H2 (R-2=0.9872), indicating that most removed NO3- was transformed to N2O and N-2 by denitrification. In PJ soil, N2O and N-2 emissions were increased significantly (P<0.05) by the addition of greater NO3- concentrations. However, N2O and N-2 emissions from PV and MV soils were increased by the addition of 0 to 5mgNL(-1), but not by 5 to 10mgNL(-1). At 10mgNL(-1), N-2 emissions for 7d were greater in PJ soil (pH 7.0) than in PV (pH 5.8) or MV (pH 4.3) soils, while N2O emissions were higher in PV and MV soils than in PJ soil. In MV soil, N2O was the main product throughout the experiment. In conclusion, NO3- concentration and soil pH affected N2O and N-2 emissions from three flooded soils.

    DOI: 10.1080/00380768.2015.1094747

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  • Combined use of sugars and nutrients derived from young maize plants for thermophilic L-lactic acid fermentation Reviewed

    S. Akao, H. Nagare, M. Maeda, K. Kondo, T. Fujiwara

    INDUSTRIAL CROPS AND PRODUCTS   69   440 - 446   2015.7

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:ELSEVIER SCIENCE BV  

    Fermentation of lignocellulosic biomass requires auxiliary materials such as nutrients for fermentation. Because of the low prices of fermentation products such as bioethanol, the costs of nutrients are not negligible. We have developed the concept of using substances natively present in lignocellulosic biomass as nutrients for the downstream fermentation. The leaves and stalks of young dent corn plants were used as biomass and the nutrients were recovered by soaking them in water before alkaline pretreatment, followed by enzymatic saccharification and fermentation. Performing thermophilic L-lactic acid fermentation using these recovered nutrients support their use as commercially feasible alternatives. A level of recovered nutrients of 40% was sufficient to support the fermentation of recovered sugars derived from the same corn biomass. However, the amount of recovered nutrients required for fermentation was almost double that when using yeast extract based on the amounts of nitrogen and/or phosphorus added. The nitrogen and phosphorus balances in the process indicated that adding nutrients was crucial for promoting fermentation based on the amounts of nitrogen and phosphorus. The nutrients proposed were considered to be effective for fermenting biomass pretreated by alkaline, dilute add, and hydrothermal methods. (C) 2015 Elsevier B.V. All rights reserved.

    DOI: 10.1016/j.indcrop.2015.02.055

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  • リン酸カルシウム沈殿生成による養豚場放流水の水質改善と溶解平衡計算 Reviewed

    永禮英明

    土木学会論文集G (環境)   71 ( 7 )   III 323-III 328   2015

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    DOI: 10.2208/jscejer.71.III_323

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  • Development of a new wastewater treatment process for resource recovery of carotenoids Reviewed

    H. Sato, H. Nagare, T. N. C. Huynh, H. Komatsu

    WATER SCIENCE AND TECHNOLOGY   72 ( 7 )   1191 - 1197   2015

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:IWA PUBLISHING  

    A new wastewater treatment process that involves coagulation, ozonation, and microalgae cultivation has been developed. Here, two challenges are discussed. The first was minimizing phosphorus removal during coagulation in order to maximize algal production. The second was to optimize microalgae cultivation; algal species that grow rapidly and produce valuable products are ideal for selection. Haematococcus pluvialis, which produces the carotenoid astaxanthin, was used. Growth rate, nutrient removal ability, and astaxanthin production of H. pluvialis in coagulated wastewater were investigated. After coagulation with chitosan, the turbidity and suspended solids decreased by 89% +/- 8.4 -> 8% and 71 -> 73% +/- 16%, respectively. The nitrogen and phosphorus contents of the supernatant remained at 86% +/- 6% and 69 -> 67% +/- 24%, respectively. These results indicate that coagulation with chitosan can remove turbidity and SS while preserving nutrients. H. pluvialis grew well in the supernatant of coagulated wastewater. The astaxanthin yield from coagulated wastewater in which microalgae were cultured was 3.26 mg/L, and total phosphorus and nitrogen contents decreased by 99.0% +/- 1.4% -> 99% + 1% and 90.3% +/- 7.6% -> 90% +/- 8% (Days 31-35), respectively.

    DOI: 10.2166/wst.2015.330

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  • Advantages of pre-harvest temporal flooding in a catch crop field in relation to soil moisture and nutrient salt removal by root uptake Reviewed

    Daisuke Yasutake, Kenkichi Awata, Keisuke Kondo, Shinzo Yamane, Masayuki Matsuoka, Morihiro Maeda, Hideaki Nagare, Ryosuke Nomiyama, Yuki Sago, Masaharu Kitano, Taku Fujiwara

    BIOLOGIA   69 ( 11 )   1577 - 1584   2014.11

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:DE GRUYTER OPEN LTD  

    Catch crop cultivation coupled with subsequent flood activity is an environmental friendly method of removing nutrient salts from soil in greenhouse. However, in comparison with the usual fallow period in greenhouse horticulture in Japan, a longer time is required for cultivation and soil drying after flooding. To minimize such time while retaining catch crop performance, temporal flooding was conducted in an experimental catch crop field of corn before harvest (i.e., pre-harvest temporal flooding), when crops were growing well and most nutrient salts within the soil had been taken up by the roots. Results showed that pre-harvest temporal flooding enhanced crop growth and stomatal opening; hence, evapotranspiration (mostly transpiration) was increased to a high value (3.5 times that of bare soil plot in greenhouse). Therefore, compared with the bare soil field, there was a remarkable pronounced decrease in the soil water content due to evapotranspirational water loss in the catch crop field after temporal flooding. Furthermore, the total nutrient (nitrogen) uptake by crops was also significantly accelerated in relation to pre-harvest flooding owing to the increase in crop growth. It was also found that electrical conductivity and nitrate nitrogen concentration of soil solution (at a soil-water ratio of 1:5) decreased with time owing to root uptake, and were at a fairly low level when pre-harvest flooding was conducted. These results suggest that pre-harvest temporal flooding shortens the implementation time by accelerating soil drying, and increases salt removal by root uptake; thus, this method delivers considerable advantages for practical use in catch crop cultivation.

    DOI: 10.2478/s11756-014-0470-9

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  • Characteristics of Nutrient Salt Uptake Associated with Water Use of Corn as a Catch Crop at Different Plant Densities in a Greenhouse

    D. Yasutake, C. Kiyokawa, K. Kondo, R. Nomiyama, M. Kitano, M. Mori, S. Yamane, M. Maeda, H. Nagare, T. Fujiwara

    PEDOSPHERE   24 ( 3 )   339 - 348   2014.6

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    Authorship:Lead author   Language:English   Publishing type:Research paper (scientific journal)   Publisher:SCIENCE PRESS  

    Dent corn, as a catch crop used for salt removal, was cultivated at different densities, i.e., 7.3 (low density), 59.7 (normal density), and 119.5 plants m(-2) (high density), during a 50 d fallow period after cultivation of a commercial crop in a greenhouse, to analyze the characteristics of nutrient salt (N, K, Mg, and Ca) uptake by roots and to study the effect of plant density on the characteristics associated with crop water use. Leaf area index for the high and normal density treatments reached extremely high values of 24.3 and 14.9, respectively. These values induced higher transpiration rates that were estimated using the Penman-Monteith model with the incorporation of specific parameters for crop and greenhouse conditions. The total N, K, Mg, and Ca contents in the crop canopy at harvest were 26.8, 13.0, 1.0, and 1.7 g m(-2), respectively, under the high density treatment. The dynamics of salt uptake rates for high, normal, and low density treatments were evaluated by assessing weekly changes in salt content, and were subsequently compared against the transpiration rate. A positive linear relationship was obtained between these 2 parameters for: all 3 density treatments and all tested salts. Hence, higher transpiration rates caused higher salt uptake rates through water absorption. On the other hand, salt uptake efficiency per unit water use by cultivation was lower in the low density treatment. Therefore, management procedures with dense planting that induce higher transpiration rates and lower evaporation rate are extremely important for the effective cultivation of corn catch crops.

    DOI: 10.1016/S1002-0160(14)60020-5

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  • EVALUATION OF GREENHOUSE GAS EMISSION, NITROGEN LOAD AND BREAK-EVEN POINT OF INTRODUCING LACTATE FERMENTATION AND CATCH CROP SYSTEM Reviewed

    MASUDA Takanori, MATSUOKA Masayuki, YAMADA Masato, HASE Takahito, AKAO Satoshi, NAGARE Hideaki, FUJIWARA Taku

    PROCEEDINGS OF ENVIRONMENTAL AND SANITARY ENGINEERING RESEARCH   70 ( 7 )   III_483-III_491 - III_491   2014

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    In previous studies, a system consisting of catch crop cultivation and lactate fermentation was proposed in order to reduce greenhouse gas emission and nitrate infiltration from agricultural field. The system also has aims of recovering nutrient and producing lactate from catch crops to gain profitable products. In this research evaluation of the amount of greenhouse gas emission, nitrogen load to water environment and break-even point of introducing the lactate fermentation system of catch crop were conducted. As a result, increased amount of greenhouse gas emission from the whole system is larger than the decreased amount of N2O gas emission from agricultural field by catch crop. Most of the nitrogen load from agricultural fields cleaned up by catch crop is discharged as waste water from lactate production process. This means non-point source pollution in the agricultural fields is transformed to point source pollution through the system. Evaluation results showed the system could help to reduce the nitrogen load on water environment using advanced wastewater treatment. From the evaluation of the production cost, we found that nutrients extracting system in the previous stage of lactate fermentation is relatively advantageous than other systems. It was found that the break-even point of the system is greater than 105tDryWeight of catch crop, which means it is greater than 18ha of cultivation area of catch crop.

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  • Cascade utilization of water chestnut: recovery of phenolics, phosphorus, and sugars Reviewed

    Satoshi Akao, Koutaro Maeda, Yoshihiko Hosoi, Hideaki Nagare, Morihiro Maeda, Taku Fujiwara

    ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH   20 ( 8 )   5373 - 5378   2013.8

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    Overgrowth of aquatic plants, such as water chestnut, has been reported as a regional problem in various areas. We proposed cascade utilization of water chestnut through the recovery of phenolics, phosphorus, and sugars. Phenolics were extracted using 50 g (wet weight) of biomass with 300 mL of acetone, methanol, or hot water, and the yields of total phenolics were 80.2, 56.2, and 49.7 mg g(-1) dry weight of native biomass, respectively. The rate of eluted phosphorus in the phenolic extraction step was 8.6, 14.8, and 45.3 % of that in the native biomass, respectively, indicating that the use of polar organic solvents suppressed phosphorus elution at the phenolic extraction step. Extraction of phosphorus following the phenolic extraction was combined with alkaline pretreatment (1 % NaOH solution) of biomass for saccharification; 64.1 and 51.0 % of phosphorus in the native biomass were extracted using acetone and methanol for the phenolic extraction, respectively. Saccharification following the alkaline pretreatment showed that the glucose recovery rates were significantly increased (p < 0.05) with the phenolic extraction step compared to alkaline pretreatment alone. This finding indicates that extraction of phenolics not only provides another useful material but also facilitates enzymatic saccharification.

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  • Seasonal changes in the performance of a catch crop for mitigating diffuse agricultural pollution Reviewed

    K. Kondo, K. Inoue, T. Fujiwara, S. Yamane, D. Yasutake, M. Maeda, H. Nagare, S. Akao, K. Ohtoshi

    Water Science and Technology   68 ( 4 )   776 - 782   2013

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    An in situ technology for mitigating diffuse agricultural pollution using catch crops was developed for simultaneously preventing nitrate groundwater pollution, reducing nitrous oxide (N2O) gas emissions, and removing salts from the topsoil. Seasonal changes in the performance of a catch crop were investigated using lysimeters in a full-scale greenhouse experiment with 50 d cultivation of dent corn. Catch crop cultivation significantly reduced the leached mineral nitrogen by 89-91% in summer, 87-89% in spring, and 61-82% in winter, and it also significantly reduced the N2O emission by 68-84% in summer. The amounts of nitrogen uptake by the catch crop were remarkably higher than those of leached nitrogen and N2O emission in each season. Catch crop cultivation is a promising technology for mitigating diffuse agricultural pollution. © IWA Publishing 2013.

    DOI: 10.2166/wst.2013.258

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  • Comparison of simultaneous and separate processes: saccharification and thermophilic L-lactate fermentation of catch crop and aquatic plant biomass Reviewed

    Satoshi Akao, Koutaro Maeda, Shingo Nakatani, Yoshihiko Hosoi, Hideaki Nagare, Morihiro Maeda, Taku Fujiwara

    ENVIRONMENTAL TECHNOLOGY   33 ( 13 )   1523 - 1529   2012

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    Catch crop candidates (corn, guinea grass) for recovering nutrients from farm soil and aquatic plants (water caltrop, water hyacinth) were utilized to produce L-lactic acid. The efficiencies of pre-treatment methods for enzymatic saccharification and L-lactate production of two fermentation processes, thermophilic simultaneous saccharification and fermentation (SSF), as well as separate saccharification and fermentation, were compared. Conditions were set at 55 degrees C and pH 5.5 for non-sterile fermentation. Alkaline/peroxide pre-treatment proved the most effective for saccharification in pre-treated corn, guinea grass, water caltrop and water hyacinth with glucose yields of 0.23, 0.20, 0.11 and 0.14 g/g-dry native biomass (24-hour incubation period), respectively. Examination of the two types of thermophilic L-lactate fermentation employed following alkaline/peroxide pre-treatment and saccharification demonstrated that the L-lactate yield obtained using SSF (0.15 g/g in the case of corn) was lower than that obtained using separate saccharification and fermentation (0.28 g/g in the case of corn). The lower yield obtained from SSF is likely to have resulted from the saccharification conditions used in the present study, as the possibility of cellulase deactivation during SSF by thermophilic L-lactate producing bacteria existed. A cellulase that retains high activity levels under non-sterile conditions and a L-lactate producer without cellulose hydrolysis activity would be required in order for SSF to serve as an effective method of L-lactate production.

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  • Reduction of Nutrient Leaching Losses by using a Catch Crop during a Fallow Period following Eggplant Production in a Greenhouse Reviewed

    MAEDA Morihiro, NAKASONE Yasuhiro, OKAMOTO Takashi, ASANO Yuichi, FUJIWARA Taku, NAGARE Hideaki, AKAO Satoshi

    PROCEEDINGS OF ENVIRONMENTAL AND SANITARY ENGINEERING RESEARCH   68 ( 7 )   III_103-III_111 - III_111   2012

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    Greenhouses are usually irrigated after cropping to remove accumulated salts in the topsoil. Nitrate remained in the soil is reported to be transported to groundwater due to the irrigation, resulting in high nitrate concentration in ground or surface waters. The present study evaluated the effect of a catch crop (dent corn) on leaching losses of nitrogen and phosphorus during a fallow period (catch crop cultivation, salt removal irrigation and reductive soil disinfection) in a farmer's eggplant greenhouse in Okayama, Japan, in 2010 and 2011. Nitrogen leaching was greatly reduced owing to the nitrogen uptake by the catch crop with compared to the control (p < 0.01). Differences of nitrogen losses during the fallow period between treatments were 12.2 g m-2 in 2010 and 5.4 g m-2 in 2011, probably due to different contents of mineral nitrogen remained in the soil after eggplant harvests. On the other hand, phosphorus leaching was not significantly different between treatments (p > 0.05). The effect of phosphorus uptake by the catch crop may be masked because of the large amount of mineral phosphorus accumulated in the soil. Our results clearly showed that catch crop growth during a fallow period reduced nitrogen leaching in the eggplant greenhouse.

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  • Nutrient recovery from biomass cultivated as catch crop for removing accumulated fertilizer in farm soil Reviewed

    H. Nagare, T. Fujiwara, T. Inoue, S. Akao, K. Inoue, M. Maeda, S. Yamane, M. Takaoka, K. Oshita, X. Sun

    WATER SCIENCE AND TECHNOLOGY   66 ( 5 )   1110 - 1116   2012

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    As a result of long-term continuous use of fertilizers in farm land, a large amount of nutrients accumulate in the soil, increasing the risk of eutrophication or nitrate pollution of groundwater. For rehabilitating the farm soil and recovering nutrients such as nitrogen, phosphorus and potassium, a new system has been developed by our research group. This paper discusses the methodology of extracting nutrients from biomass in order to recover phosphorus and other nutrients in crystal form. Around 80% or higher extraction rates were achieved for phosphorus and potassium by soaking the powdered tissue in distilled water or 1% NaOH solution for 24 h. The extracted phosphorus and potassium act as a potential resource for recycled fertilizer or other industrial materials.

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  • Analysis of Water Contamination in Kasaoka-Bay Reclaimed Fields by Using Stable Isotope Natural Abundances Reviewed

    Maeda, K, Akao, S, Hosoi, Y, Nagare, H, Maeda, M, Fujiwara, T

    Doboku Gakkai Ronbunshuu G   67 ( 7 )   III_213 - III_222   2011.11

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  • Behavior of inorganic elements during sludge ozonation and their effects on sludge solubilization Reviewed

    Pengzhe Sui, Fumitake Nishimura, Hideaki Nagare, Taira Hidaka, Yuko Nakagawa, Hiroshi Tsuno

    WATER RESEARCH   45 ( 5 )   2029 - 2037   2011.2

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    The behavior of inorganic elements (including phosphorus, nitrogen, and metals) during sludge zonation was investigated using batch tests and the effects of metals on sludge solubilization were elucidated. A decrease of similar to 50% in the ratio of sludge solubilization was found to relate to a high iron content 80-120 mgFe/gSS than that of 4.7-7.4 mgFe/gSS. During sludge zonation, the pH decreased from 7 to 5, which resulted in the dissolution of chemically precipitated metals and phosphorus. Based on experimental results and thermodynamic calculation, phosphate precipitated by iron and aluminum was more difficult to release while that by calcium released with decrease in pH. The release of barium, manganese, and chrome did not exceed 10% and was much lower than COD solubilization; however, that of nickel, copper, and zinc was similar to COD solubilization. The ratio of nitrogen solubilization was 1.2 times higher than that of COD solubilization (R(2) = 0.85). Of the total nitrogen solubilized, 80% was organic nitrogen. Because of their high accumulation potential and negative effect on sludge solubilization, high levels of iron and aluminum in both sewage and sludge should be considered carefully for the application of the advanced sewage treatment process with sludge zonation and phosphorus crystallization. (C) 2010 Elsevier Ltd. All rights reserved.

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  • ソフトバイオマスを原料とした酵素糖化における各種前処理の糖化効率比較

    前田光太郎, 赤尾聡史, 細井由彦, 永禮英明, 前田守弘, 藤原拓

    土木学会論文集G   67 ( 7 )   III_433-III_440   2011

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  • Construction and Validation of Lake Biwa Basin Simulation Model with Integration of Three Components of Land, Lake Flow, and Lake Ecosystem

    SATO Yuichi, KOMATSU Eiji, NAGARE Hideaki, UEHARA Hiroshi, YUASA Takashi, OKUBO Takuya, OKAMOTO Takahiro, KIM Jaegyu

    Japan journal of water pollution research   34 ( 9 )   125 - 141   2011

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    To understand the phenomena occurring in Lake Biwa and predict the effects of measures for improving water quality, constructing a simulation model that can calculate the hydrological and material cycle and reaction process in the basin with high accuracy is the most effective way. In this study, a Lake Biwa Basin simulation model with the integration of three components of land, lake flow, and lake ecosystem is constructed and named "Lake Biwa Basin Hydrological and Material Cycle Simulation Model". Distributed and 3-dimensional models are adopted; these models can simulate water quality and quantity unsteadily by considering weather, social conditions, and so on. As a result, river discharge and quality in main rivers, such as Yasu River and Hino River, and water temperature, average quality and seasonal variation in the lake are adequately calculated. On the other hand, it is insufficient to calculate water quality of the time series and distribution in Southern Lake; thus, it is a future challenge to evaluate spatial-temporal lake water quality precisely.

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  • 回収・再資源化を目的としたバイオマスからの元素抽出

    永禮英明, 藤原拓, 赤尾聡史, 前田守弘, 山根信三

    土木学会論文集G   67 ( 7 )   III_461-III_466   2011

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  • Analyzing evapotranspiration components and crop coefficients for catch crop field with small area at different plant densities in a greenhouse Reviewed

    Daisuke Yasutake, Chiyo Kimura, Keisuke Kondo, Kenta Inoue, Makito Mori, Shinzo Yamane, Morihiro Maeda, Hideaki Nagare, Taku Fujiwara

    Environmental Control in Biology   49 ( 4 )   217 - 225   2011

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    We cultivated dent corn as a catch crop for controlling soil salt conditions in field plots at different densities, namely, 7.3 (low), 59.7 (normal) and 119.5 (high) plants m -2 in a greenhouse, where environmental elements and plant growth were measured for analyses of evapotranspiration components relating to the catch crop effects. Using the Penman-Monteith model with specific parameters incorporated for the crop and greenhouse, leaf transpiration and soil evaporation were estimated. Further crop coefficients were analyzed by dividing actual evapotranspiration by a reference evapotranspiration determined from meteorological data. Leaf area index for the normal and high density treatments reached 14 and 22, respectively, which were extremely high values compared to those for various other crops. Transpiration and its ratio to evapotranspiration increased with plant growth and density. Crop coefficients also increased with leaf area index and transpiration, and the coefficients for the normal and high density treatments reached high values of 1.5-2 and 2-3, respectively. These findings reveal characteristic features of plant growth and water dynamics in a catch crop field. The results of this study will contribute to the optimization of catch crop cultivation and to elucidate the crop's effects on soil salt conditions in greenhouses.

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  • クリーニングクロップ栽培と湛水の組み合わせによるハウス土壌集積塩類の除去特性

    井上賢大, 近藤圭介, 藤原 拓, 前田守弘, 高岡昌輝, 大年邦雄, 山根信三, 永禮 英明, 赤尾聡史

    環境工学論文集   47   273 - 280   2010

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  • トウモロコシからのリン抽出方法の検討

    永禮英明, 井上 司, 藤原 拓, 赤尾聡史, 前田守弘, 山根信三

    環境工学論文集   47   459 - 464   2010

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  • オゾンによる汚泥減容化とリン回収を導入した高度下水処理プロセスでのリン回収方法の検討

    永禮英明, 津野 洋, W. Saktaywin, 早山 恒成

    環境工学論文集   46   469 - 475   2009

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  • Influence of the Surrounding Water Environment on Mire Vegetation

    Tachibana, H, Narumi, K, Kuchimachi, S, Saito, M, Tatsumi, K, Nagare, H

    Journal of Water and Environment Technology   7 ( 2 )   103 - 108   2009

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    Mires are loosing their natural state as a result of human activities. Recently natural Sphagnum mires in Hokkaido, Japan, have been disappearing as a result of the proliferation of alders. Here we show that such proliferation is caused by the inflow of phosphorous compounds as non-point pollutants. Those phosphorous compounds flow in from agricultural fields around mires. The constituents of groundwater or surface water make alders proliferate rapidly. Phosphorous, a typical non-point-polluting nutrient, contributes to the growth of alders, which assimilate atmospheric nitrogen.

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  • Removal of Humic Substances by Repeated Mixing with PACl

    Nagare, H, Aso, T, Yoshida, S, Ebie, K

    Water Practice and Technology   4 ( 2 )   2009

  • Sludge ozonation and its application to a new advanced wastewater treatment process with sludge disintegration

    Hideaki Nagare, Hiroshi Tsuno, Wilasinee Saktaywin, Tsunenari Soyama

    OZONE-SCIENCE & ENGINEERING   30 ( 2 )   136 - 144   2008.3

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    The applicability of sludge ozonation on wastewater treatment processes was investigated to reduce the amount of excess sludge without losing phosphorus removal efficiency. Solubilization degree per ozone consumption for general sludge was in the range from 2.4 to 5.8 gSS/O-3 and from 4.1 to 7.7 gCOD/gO(3). Around 80 to 90% of solubilized organics was biodegradable at a solubilization degree of 0.3. Based on the experimental results, a lab-scale plant with sludge ozonation and phosphorus crystallization was constructed to investigate the treatment performance. Amount of excess sludge was reduced by 93% with almost complete removal of soluble BOD and phosphorus removal efficiency of more than 80%. The percentage of the effluent CODCr discharge increased from 10% to 14-17% after installing ozonation and crystallization because of the formation of non-biodegradable organic substances in ozonation process. Energy consumption of the innovative advanced process is comparable or can be even smaller than that of the conventional anaerobic/oxic (A/O) process in spite of the installation of ozonation and crystallization.

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  • Advanced sewage treatment with ozone under excess sludge reduction, disinfection and removal of EDCs

    Hiroshi Tsuno, Kiyomi Arakawa, Yasuhiro Kato, Hideaki Nagare

    OZONE-SCIENCE & ENGINEERING   30 ( 3 )   238 - 245   2008

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    A new advanced treatment system, which consists of biological nutrient removal process combined with reduction of excess sludge by ozonation and phosphorus recovery by crystallization and polishing-up ozonation process, was developed based on the fundamental studies and demonstrated by the demonstration plant set in AICHI EXPO 2005. Reduction of withdrawn excess sludge by 90% and phosphorus recovery by 70% were accomplished without any adverse effects on biological nutrient removal. The concentrations of SS, BOD, T-P and T-N in the effluent were less than 1.0, 3.0, 0.5 and 10 mg/L, respectively. EDCs were reduced to almost undetectable level and 2-log disinfection of Bacillus subtilis was established. The energy amount required for the operation was saved by 40% when compared with a conventional system to get the same level of water quality.

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  • 瀬戸内海におけるPCBの分布とムラサキイガイへの濃縮特性に関する研究

    津野 洋, 新海貴史, 中野 武, 永禮英明, 松村千里, 是枝卓成

    土木学会論文集G   63 ( 2 )   149 - 158   2007

  • 汚泥削減・リン回収型生物学的下水高度処理プロセスの開発

    津野 洋, 永禮英明, W. Saktaywin, 早山恒成

    下水道協会誌論文集   44   151 - 163   2007

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  • Composition Properties and Origin Presumption of PCBs in Seto Inland Sea

    TSUNO Hiroshi, SHINKAI Takashi, NAKANO Takeshi, NAGARE Hideaki

    Japan journal of water pollution research   30 ( 8 )   457 - 462   2007

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    The concentrations of PCBs in sea water and blue mussels ranged from 0.5 to 4.0 ng · l-1 (mean ± S.D.: 1.8 ± 0.6 ng · l-1) and from 3.1 to 69.8 ng · g-1 -wet (24.0 ± 19.0 ng · g-1-wet), respectively, in the Seto Inland Sea. The main homologues of PCB in seawater and blue mussels were T4CBs and H6CBs, respectively, and their content ratios to total PCB were 40∼50%. Homologues with high chlorine content accumulated in blue mussels. By principal component analyses associated with the homologues of PCB in seawater, blue mussels and sediment, it was clearly shown that the sea area in Osaka Bay and Harima-nada were mainly contaminated with low-chlorine-content homologues of PCB which were mainly used in condenser and heating fluid, and that the other sea area was mainly contaminated with high-chlorine-content homologues which were mainly used in paints and varnish. More detailed analyses were possible by the principal component analyses with selected and important isomer data.

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  • 琵琶湖流域水物質循環モデルの構築と複数年次における結果の検証

    佐藤 祐一, 金 再奎, 高田 俊秀, 永禮 英明, 小松 英司, 湯浅 岳史, 上原 浩

    日本陸水学会 講演要旨集   72   36 - 36   2007

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    DOI: 10.14903/jslim.72.0.36.0

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  • Lake Biwa Basin Hydrological and Material Cycle Simulation Coupling Land, Lake Flow, Lake Ecosystem Models

    SATO YUICHI, KIM JAEGYU, TAKADA TOSHIHIDE, NAITO MASAAKI, NAGARE HIDEAKI, KOMATSU EIJI, YUASA TAKASHI, UEHARA HIROSHI

    Proceeding of Annual Conference   20   90 - 90   2007

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  • POPsの二枚貝への濃縮特性に関する研究 Reviewed

    津野洋, 中野武, 永禮英明, 松村千里, 鶴川正寛, 是枝卓成, 高部祐剛

    土木学会論文集G   63   179 - 185   2007

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  • Operation of a new sewage treatment process with technologies of excess sludge reduction and phosphorus recovery

    W. Saktaywin, H. Tsuno, H. Nagare, T. Soyarna

    WATER SCIENCE AND TECHNOLOGY   53 ( 12 )   217 - 227   2006

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    This paper shows the potential application of a new sewage treatment process with technologies of excess sludge reduction and phosphorus recovery. The process incorporated ozonation for excess sludge reduction and crystallisation process for phosphorus recovery to a conventional anaerobic/oxic (A/O) phosphorus removal process. A lab-scale continuous operation experiment was conducted with the ratio of sludge flow rate to ozonation tank of 1.1% of sewage inflow under 30 to 40 mgO(3)/gSS of ozone consumption and with sludge wasting ratio of 0.34% (one-fifth of a conventional NO process). Throughout the operational experiment, a 60% reduction of excess sludge production was achieved in the new process. A biomass concentration of 2,300 mg/L was maintained, and the accumulation of inactive biomass was not observed. The new process was estimated to give a phosphorus recovery degree of more than 70% as an advantage of excess sludge reduction. The slight increase in effluent COD was observed, but the process performance was maintained at a satisfactory level. These facts demonstrate an effectiveness of the new process for excess sludge reduction as well as for phosphorus recovery.

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  • Development of Resource Recycling Type Urban Wastewater and Solid Waste Processing System

    TSUNO Hiroshi, NAGARE Hideaki, HIDAKA Taira

    Journal of The Society of Instrument and Control Engineers   45 ( 10 )   851 - 856   2006

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    DOI: 10.11499/sicejl1962.45.851

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  • Advanced sewage treatment process with excess sludge reduction and phosphorus recovery

    W Saktaywin, H Tsuno, H Nagare, T Soyama, J Weerapakkaroon

    WATER RESEARCH   39 ( 5 )   902 - 910   2005.3

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    An advanced sewage treatment process has been developed, in which excess sludge reduction by ozonation and phosphorus recovery by crystallization process are incorporated to a conventional anaerobic/oxic (A/O) phosphorus removal process. The mathematical model was developed to describe the mass balance principal at a steady state of this process. Sludge ozonation experiments were carried out to investigate solubilization characteristics of sludge and change in microbial activity by using sludge cultured with feed of synthetic sewage under A/O process. Phosphorus was solubilized by ozonation as well as organics, and acid-hydrolyzable phosphorus (AHP) was the most part of solubilized phosphorus for phosphorus accumulating organisms (PAOs) containing sludge. At solubilization of 30%, around 70% of sludge was inactivated by ozonation. The results based on these studies indicated that the proposed process configuration has potential to reduce the excess sludge production as well as to recover phosphorus in usable forms. The system performance results show that this system is practical, in which 30% of solubilization degree was achieved by ozonation. In this study, 30% of solubilization was achieved at 30 mg O-3/gSS of ozone consumption. (c) 2005 Elsevier Ltd. All rights reserved.

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  • 余剰汚泥発生抑制・リン回収型生物学的栄養塩除去法による下水からのリンの回収

    津野 洋, 永禮英明

    再生と利用   28 ( 110 )   31 - 34   2005

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  • Evaluation of Nitrification Effects on BOD by Batch Experiments

    FUJII Shigeo, Matsuzawa Masaki, Nagare Hideaki, Shimizu Yoshihisa

    Doboku Gakkai Ronbunshuu G   40   531 - 540   2003

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    Effects of nitrification on BOD were evaluated with two kinds of batch experiments, and the problems caused by N-BOD were discussed with descriptions of test manuals, experimental data and literature review. The main results drawn in this study are as follows:(1) most of water analysis manuals do not clearly describe nitrification on BOD test is an interference nor the matter to be measured, (2) ammonium nitrogen in dilution water causes a positive error in BOD test, and can overestimate N-BOD values more than two times, (3) BOD values measured with present methods can not express the pollution level because of N-BOD appearance during the purification development. As a conclusion, it is recommended that oxygen consumption by nitrification should be eliminated from the contents of BOD, and the test procedure should adapt an inhibition process for nitrification in BOD measurement.

    DOI: 10.11532/proes1992.40.531

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  • Nitrogen Mass Change and Cycle in Lake Biwa

    NAGARE Hideaki, FUJII Shigeo, SOMIYA Isao

    Journal of Japan Society on Water Environment   26 ( 10 )   663 - 669   2003

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    The mass change of nitrogen in Lake Biwa was shown, and its cycle was discussed and compared with the input/output loading. Nitrogen exists at 10.5X103 ton in average, and its minimum and maximum mass are 7.6X103 ton, 13.4X103 ton, respectively. Its average mass is equivalent to 133% of the annual input loading, resulting in 1.6 months of residence time, which is shorter than 5.5 years of hydraulic retention time. This indicates that nitrogen in the lake is removed by settling onto the lake bottom or denitrification, and the removed mass is estimated to be 71% of the input loading. Phytoplanktons mainly utilize ammonium nitrogen in epilimnion whose mass is only 1% of the total mass in the lake. rather than other inorganic nitrogen amounting to more than ten-fold of ammonium nitrogen. During the stratification period, almost all decomposed nitrogen in the organic matter is oxidized into nitrate, and half of them is likely to be removed by denitrification.

    DOI: 10.2965/jswe.26.663

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  • 森林河川水質と集水域内地質・植生との関係の評価

    永礼英明, 藤井滋穂, 宗宮 功, 芹澤佐和子

    環境工学論文集   40   501 - 506   2003

  • Nutrient Mass Estimation in Lake Biwa

    NAGARE Hideaki, SOMIYA Isao, FUJII Shigeo

    Japan journal of water pollution research   25 ( 10 )   599 - 604   2002

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    The estimation of material mass in bodies of water such as lakes provides much information on water quality formation mechanism since it enables evaluation of mass balance in the body of water examined. However, such estimation is difficult, because water quality is not uniform and a precise water quality survey is actually difficult in a large lake. In this paper, mass estimation methods are proposed and compared with each other. In each method, material mass in Lake Biwa, Japan was estimated based on water quality data at 75 points in the lake. The spline technique that interpolates the concentration value in 500X500X1m-size mesh in the lake with a σ value of 0.3 was selected as the most suitable estimation method. Judging from the N/P ratio, mass values estimated by this technique were more reliable than those reported previously. Nitrogen and phosphorus are present in Lake Biwa at 7.6-13X103 tonN and 190-340 tonP, respectively, and their averages in 20 surveys from 1995 until 2000 were 11X103 tonN and 230 tonP, respectively.

    DOI: 10.2965/jswe.25.599

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  • Effects of Cold Winter on Seasonal Water Quality Change in Lake Biwa

    Nagare, H, Somiya, I, Fujii, S, Morita, M

    Advances in Asian Environmental Engineering   1 ( 1 )   47 - 53   2001

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  • Water quality characteristics of forest rivers around Lake Biwa

    S Fujii, Somiya, I, H Nagare, S Serizawa

    WATER SCIENCE AND TECHNOLOGY   43 ( 5 )   183 - 192   2001

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    Language:English   Publishing type:Research paper (scientific journal)   Publisher:I W A PUBLISHING  

    Forest river surveys were carried out at upper streams of several rivers in the Lake Biwa watershed to understand the water quality characteristics of the rivers, and to find out their relationships with forest features such as geographical. geological and vegetational data. The results showed: (1) Forests have some purification functions for nitrogen and organic matter. but become sources for most of ionic species. (2) Main mineral species in forest rivers are Ca2+, Mg2+ and Na+, HCO3-, CO32-, Cl-, SO42- and SiO2. (3) Loading from forests was 0.4-7 kg/km(2)/d for TN and 0.01-0.3 kg/km(2)/d for TP. (4) River quality reflects the properties of each forest, and is unique to the place, especially in ionic species such as Ca2+ and Cl-. (5) A cluster analysis successfully categorized ionic components into several groups.

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  • Phosphorus mass-quantity change in Lake Biwa

    H Nagare, Somiya, I, S Fujii, M Morita

    WATER SUPPLY AND WATER QUALITY   1 ( 2 )   49 - 56   2001

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    To understand the eutrophication phenomena in Lake Biwa, Japan, a research project for the water quality formation processes was executed. This paper presents phosphorus mass changes in water body in Lake Biwa from April 1995 to January 2000 and discusses the main factors of the change, Phosphorus mass ranged from 190 to 350 t, with an average of 260 t. DP mass in 1995, '97 and '98 showed seasonal change patterns, while non-periodical phenomena seemed to control the PP mass. Phosphorus mass was increased about 15 t in epilimnion from April to July while nitrogen showed a 50 t decrease. This disagreement suggests that some processes selectively accumulated phosphorus in epilimnion during this period. However, such an increase in phosphorus was not observed in 1996 and '99. Air temperature was lower and much snowfall was recorded in 1996 and '99, suggesting that coldness in winter season weakened the phosphorus accumulation process to depress the mass in epilimnion in summertime. Water temperature increase seemed to be delayed in proportion to total snowfall, but thermocline was formed independently of coldness. Hence, the idea was abandoned that the delay of thermocline formation encouraged the sedimentation process, and biological activities were considered to be the main factor controlling phosphorus mass in the epilimnion in Lake Biwa.

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  • Changes in water quality due to leaves of aquatic macrophyte and their periphytons

    NAGARE Hideaki, YOSHIZAWA Kaori, TACHIBANA Harukuni

    Doboku Gakkai Ronbunshuu G   33   349 - 354   1996

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    Publisher:Japan Society of Civil Engineers  

    Aquatic macrophytes form a "system" consisting of the macrophytes themselves and periphytons attached to them. The system has a significant role in purifying water. In this study, we evaluated such water purification functions of macrophytes-periphytons "system", as removing nutrients of the river water prior the river flowing into a lake. Using the data obtained by a field survey and laboratory tests, we made a model of the water quality purification by macrophytes and the periphytons. As a result, we found (1) the "system" of aquatic macrophytes and periphytons play a role as "catalysis" to suspend the dissolved nutrients, and (2) a physical purification function by the aquatic macrophytes which act as a filter to remove suspended solid from the water. Also, we clarified the efficiency of these functions at the water surface.

    DOI: 10.11532/proes1992.33.349

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Books

  • 『中国の環境政策』 第9章 環境政策の汚染物質排出量削減効果

    京都大学学術出版会  2008  ( ISBN:9784876987382

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MISC

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Presentations

  • Management of phosphorus in watershed for sustainable food supply and environmental protection

    Nagare, Hideaki

    Polish-Japanese Workshop on Circular Economy in Agriculture and Agro Industry  2023.9.15 

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    Event date: 2023.9.15

    Language:English  

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  • リン回収普及に向けた微細藻類カロテノイド生産技術の開発状況

    永禮英明, 枡田隆広, 石川千遥, Huyhn Tan Nhu, 赤尾聡史, 高部祐剛

    第60回下水道研究発表会  2023.8 

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    Event date: 2023.8

    Language:Japanese  

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  • Evaluation of the Degradation Performance of Pharmaceuticals in Environmental Water by Multi-wavelength UV Irradiation and the Estimation of Their Degradation Pathways

    Hashiguchi, Ayumi, Kaneko, Hitoshi, Taniguchi, Shogo, Tada, Yuto, Klon D.C. HINNEH, Echigo, Shinya, Nagare, Hideaki

    Water and Environment Technology Conference  2023.7 

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    Event date: 2023.7

    Language:English  

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  • オゾンを用いた下水中微細藻類ヘマトコッカス優占培養法の検討

    永禮英明, 石川千遥, 枡田隆広, Huyhn Tan Nhu

    第32回日本オゾン協会年次研究講演会  2023.6 

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    Event date: 2023.6

    Language:Japanese  

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  • 資源回収型下水処理プロセスの開発に向けたHaematococcus lacustris優占培養法の検討

    石川千遥, Huyhn Tan Nhu, 永禮英明, 枡田隆広

    第57回日本水環境学会年会  2023.3 

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    Event date: 2023.3

    Language:Japanese  

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  • Wastewater treatment process with astaxanthin production by microalgae aiming at spontaneous phosphorus recycling

    IWA 2nd Resource Recovery Conference  2017 

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    Event date: 2017

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  • イミダゾリウム系イオン液体とオゾンとの反応機構

    日本オゾン協会第 26 回年次研究講演会  2017 

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  • Coagulation with chitosan as the pre-treatment for algae cultivation in wastewater

    2017 International Environmental Engineering Conference  2017 

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  • 流域社会と湖内生態系におけるリンフローの把握

    第20回日本水環境学会シンポジウム  2017 

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  • Coagulation with chitosan as the pre-treatment for algae cultivation in wastewater

    2017 International Environmental Engineering Conference  2017 

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  • Wastewater treatment process with astaxanthin production by microalgae aiming at spontaneous phosphorus recycling

    IWA 2nd Resource Recovery Conference  2017 

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  • 琵琶湖水質の将来予測シミュレーションについて⑵ ~湖沼生態系モデルの成果と今後の課題~

    第51回日本水環境学会年会  2017 

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  • 琵琶湖水質の将来予測シミュレーションについて⑴ ~第7 期湖沼水質保全計画の結果から~

    第51回日本水環境学会年会  2017 

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  • イミダゾリウム系イオン液体のオゾン分解

    第25回日本オゾン協会年次研究講演会  2016 

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  • 藻類培養のためのキトサンによる下水凝集処理

    第49回日本水環境学会年会  2015 

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  • 流域におけるリン資源管理に向けて

    北海道大学第23回衛生工学シンポジウム  2015 

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  • Astaxanthin production from wastewater by Haematococcus pluvialis

    1st IWA Resource Recovery Conference  2015 

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  • 滋賀県におけるリンのフロー

    第37回 京都大学環境衛生工学研究会シンポジウム  2015 

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  • 塩基性条件下におけるイオン液体1-butyl-3-methylimidazoulium chlorideのオゾン処理副生成物の分析

    第49回日本水環境学会年会  2015 

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  • Degradation of an ionic liquid, 1-butyl-3-methylimidazolium chloride, by ozonation

    IWA World Water Congress & Exhibition  2014 

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  • Recovery of Phosphorus and Potassium from Corn Biomass as a Magnesium Salt

    9th IWA International Symposium on Waste Management Problems in Agro-Industries  2014 

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  • Non-sterile simultaneous saccharification and fermentation of corn biomass to L-lactic acid without external nutrient addition

    9th IWA International Symposium on Waste Management Problems in Agro-Industries  2014 

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  • Ozonation of ionic liquid 1-butyl-3-methylimidazolium chloride under basic condition

    248th ACS National Meeting  2014 

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  • Characteristics of Salt Absorption by Roots of Corn Catch Crop at Different Densities in a Greenhouse

    3rd BioHydrology Conference  2013 

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  • Characteristics of Salt Absorption by Roots of Corn Catch Crop at Different Densities in a Greenhouse

    3rd BioHydrology Conference  2013 

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  • Utilization of nutrients extracted from plant biomass in thermophilic L-lactic acid fermentation

    13th World Congress on Anaerobic Digestion  2013 

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  • 温室内の異なる栽植密度条件下におけるクリーニング作物の塩類吸収特性

    日本農業気象学会2013年全国大会  2013 

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  • 植物系バイオマスの糖と栄養素を利用した高温L-乳酸発酵

    第50回環境工学研究フォーラム  2013 

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  • バイオ炭および緑肥の土壌混和が水分保持,温室効果ガス発生に及ぼす影響

    第50回環境工学研究フォーラム  2013 

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  • 植物系バイオマスからのリン,カリウム同時回収の検討

    第50回環境工学研究フォーラム  2013 

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  • クリーニングクロップとしてのレモングラスの適用性~ポット試験による評価~

    第16回日本水環境学会シンポジウム  2013 

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  • 釧路湿原温根内地域の地下水水質の分布特性

    第16回日本水環境学会シンポジウム  2013 

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  • 高知県の施設園芸を対象としたクリーニングクロップによる潜在的窒素回収量の推算

    地理情報システム学会 第22回研究発表大会  2013 

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  • Phosphorus recovery from wastewater and farmland and its potential effect in Japan

    The 2013 International Conference on the “Challenges in Environmental Science and Engineering”  2013 

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  • Utilization of nutrients extracted from plant biomass in thermophilic L-lactic acid fermentation

    13th World Congress on Anaerobic Digestion  2013 

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  • 農業系面源汚染抑制と資源回収を同時に実現する植物浄化技術の開発

    第35回 京都大学環境衛生工学研究会シンポジウム  2013 

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  • Seasonal change in diffuse agricultural pollution control performance of catch crop

    8th IWA World Water Congress & Exhibition  2012 

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  • 施設栽培休閑期におけるN2O発生要因の室内培養実験による検討

    第49回環境工学研究フォーラム  2012 

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  • Seasonal change in diffuse agricultural pollution control performance of catch crop

    8th IWA World Water Congress & Exhibition  2012 

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  • Nutrient extraction from biomass derived in water quality management countermeasures

    8th IWA World Water Congress & Exhibition  2012 

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  • 琵琶湖における第6期湖沼水質保全計画の策定について(2)~現況再現と将来予測シミュレーションの概要~

    第46回日本水環境学会年会  2012 

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  • 牛舎由来のアンモニアが隣接圃場におよぼす影響:笠岡湾干拓地における一事例

    日本土壌肥料学会2012年度鳥取大会  2012 

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  • Nutrient extraction from biomass derived in water quality management countermeasures

    8th IWA World Water Congress & Exhibition  2012 

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  • 高知県の施設園芸を対象とした資源回収作物による窒素回収量の推算

    第5回四国GISシンポジウム  2012 

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  • 水生植物ヒシのカスケード利用:ポリフェノール,栄養塩,糖の回収

    第45回日本水環境学会年会  2011 

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  • 温室内での異なる植栽密度のクリーニング作物の栽培における蒸散,蒸発および作物係数の評価

    日本農業気象学会中国四国支部大会  2011 

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  • Extraction of Nutrients in Macrophyte for Recycling

    14th World Lake Conference  2011 

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  • ライシメーターでの短期栽培によるクリーニングクロップの土壌浄化効果の評価

    第45回日本水環境学会年会  2011 

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  • 琵琶湖の物質循環のシミュレーションと汚濁負荷削減効果の考察

    第45回日本水環境学会年会  2011 

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  • クリーニングクロップ栽培によるハウス土壌の面的浄化効果の評価

    第45回日本水環境学会年会  2011 

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  • 畜産パーラー排水の凝集処理

    第44回日本水環境学会年会  2010 

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    Event date: 2010

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  • 資源回収を目的とした植物中窒素・リン抽出方法の検討

    第44回日本水環境学会年会  2010 

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  • 釧路湿原の地下水特性と植生への影響

    第44回日本水環境学会年会  2010 

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  • Development of POPs monitoring method in water area with bivalves as a bioindicator

    Environmental & sanitary engineering research  2007.7 

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    Event date: 2007.7

    Language:Japanese  

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Awards

  • 日本オゾン協会論文賞

    2009  

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  • 京都大学環境衛生工学研究会 第1回優秀プロジェクト賞

    2004  

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Research Projects

  • Microalgae cultivation in wastewater for the recovery of phosphorus ans astaxanthin

    Grant number:16K00585  2016.04 - 2019.03

    Japan Society for the Promotion of Science  Grants-in-Aid for Scientific Research  Grant-in-Aid for Scientific Research (C)

    NAGARE Hideaki

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    Grant amount:\4810000 ( Direct expense: \3700000 、 Indirect expense:\1110000 )

    To sustain the food production in the growing population and resource depletion, a new wastewater treatment process with microalgae cultivation to recover phosphorus and also a valuable product, astaxanthin in this research. Haematococcus pluvialis was used as an algae. H. pluvialis showed stronger resistant ability against ozone compared with other microbes including bacteria. The procedure for extracting and recovering phosphorus and axtaxanthin from the algal cells was also investigated.

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  • Study on practical application of semi-continuous L-lactate fermentation of biomass resources without sterile condition

    Grant number:18560530  2006 - 2008

    Japan Society for the Promotion of Science  Grants-in-Aid for Scientific Research  Grant-in-Aid for Scientific Research (C)

    TSUNO Hiroshi, YAMADA Harumi, NISHIMURA Fumitake, NAGARE Hideaki, HIDAKA Taira

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    Grant amount:\3900000 ( Direct expense: \3300000 、 Indirect expense:\600000 )

    生ごみを対象にした効率的な非滅菌条件下でのL-乳酸発酵技術を開発した。55℃の高温酸発酵ではpH 5~6の条件により、長期間にわたり安定して高光学純度のL-乳酸が生成できた。pH調整剤の検討を行い、55℃、pH5.5の培養条件下で、アンモニア、水酸化ナトリウム、水酸化カルシウムのいずれを用いても乳酸発酵を行えた。菌叢解析によりBacillus coagulansが独占して同定された。グルコースや乳酸による阻害影響を表す定数を算出し数理モデルを構築したところ、実験結果がおおむね再現された。

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  • Study on Construction and utilization of a comprehensive lake water quality database system

    Grant number:14550543  2002 - 2003

    Japan Society for the Promotion of Science  Grants-in-Aid for Scientific Research  Grant-in-Aid for Scientific Research (C)

    FUJII Shigeo, NAGARE Hideki, SHIMIZU Yoshihisa, TSUNO Hiroshi

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    Grant amount:\3500000 ( Direct expense: \3500000 )

    Monitoring is a fundamental step to understand water quality conditions in lakes, and many lakes have been storing a huge amount of water quality data. However, these past records are not effectively used. This research project aims to develop a new water quality database system, which possesses almost all data recorded in a target lake with functions to use them skillfully, and satisfies not only the general public, but also specialists. Lake Biwa was chosen as the research lake.
    Then, past and present investigation projects in Lake Biwa were surveyed and their water quality data were collected and analyzed.
    The results indicate these investigations have various and different patterns on their investigation methods; the number of sampling stations ranges 1 to 5, that of depths ranges 1 to 12, that of times in a year ranges 1 to 365, and that of measured items ranges 8 to 100 more. The whole projects identified 86 different sampling stations and 44 different depths in the lake. The variety of investigation methods suggested that simple spread sheet can not handle the whole data systematically, and that the use of a relational database application software is needed. Then, Access 2000 was introduced to organize all of the data.
    The constructed database consists of one main table, two sub-main tables and seven minor explanatory tables, and has stored 670,000 WQI data for 50,000 samples from 15 survey projects. Its application softwares were also developed with the help of VBA (Visual Basic for Application) for general users who are not familiar to Access. This system has high flexibility on the data management and application, so that further extension of the system can be easily achieved.

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  • Practice in English Presentation (2023academic year) Prophase  - 金7~8

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  • Water Quality (2023academic year) 1st semester  - 月1~2,木1~2

  • Water Quality A (2023academic year) 1st semester  - 月1,木1

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  • Seminar in Water Environment and Sanitation (2023academic year) Prophase  - その他

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  • Water supply engineering (2023academic year) Third semester  - 金3~4

  • Special Research (2023academic year) Year-round  - その他

  • Advanced Study (2023academic year) Other  - その他

  • Seminar in Environmental Management (2023academic year) Prophase  - その他

  • Seminar in Environmental Management (2023academic year) Late  - その他

  • Environmental Chemistry (2023academic year) Second semester  - 金3~4

  • Environmental Microbiology (2023academic year) Fourth semester  - 水7~8

  • Environmental Physical Chemistry (2023academic year) 1st semester  - 水1~2

  • Environmental physical chemistry A (2023academic year) 1st semester  - 水1~2

  • Environmental physical chemistry B (2023academic year) Second semester  - 金3~4

  • Foundation of environmental sanitation A (2023academic year) Concentration  - その他8~9

  • Test Methods for Environmental Sanitation and Experiments (2023academic year) 3rd and 4th semester  - 火6,火8

  • Experiments on environmental sanitation (2023academic year) 3rd and 4th semester  - 火6,火8

  • Environmental engineering mathematics IA (2023academic year) Second semester  - 金1~2

  • Environmental engineering mathematics IB (2023academic year) Fourth semester  - 水5~6

  • Linear Algebra (2023academic year) 1st and 2nd semester  - 金5~6

  • Linear Algebra (2023academic year) 1st and 2nd semester  - 金5~6

  • Linear Algebra 1 (2023academic year) 1st semester  - 金5~6

  • Linear Algebra 2 (2023academic year) Second semester  - 金5~6

  • Practice in English Presentation (2023academic year) Prophase  - 金7~8

  • Wastewater engineering (2022academic year) Third semester  - 火8~9

  • Exercise in Basic English (2022academic year) Third semester  - 金1

  • Exercise in Basic English (2022academic year) Fourth semester  - 金1

  • Practice in Building Equipment Design and Planning IA (2022academic year) special  - その他

  • Practice in Building Equipment Design and Planning IB (2022academic year) special  - その他

  • Practice in Building Equipment Design and Planning IIA (2022academic year) special  - その他

  • Practice in Building Equipment Design and Planning IIB (2022academic year) special  - その他

  • Water Treatment Engineering (2022academic year) Prophase  - 火5~6

  • Advanced Course on Water Treatment Engineering (2022academic year) Prophase  - その他

  • Water Quality A (2022academic year) 1st semester  - 水5~6

  • Water Quality B (2022academic year) Second semester  - 水5~6

  • Seminar in Water Environment and Sanitation (2022academic year) Late  - その他

  • Seminar in Water Environment and Sanitation (2022academic year) Prophase  - その他

  • Seminar in Water Environment and Sanitation (2022academic year) Prophase  - その他

  • Seminar in Water Environment and Sanitation (2022academic year) Late  - その他

  • Water supply engineering (2022academic year) Second semester  - 金5~6

  • Special Research (2022academic year) Year-round  - その他

  • Seminar in Environmental Management (2022academic year) Late  - その他

  • Seminar in Environmental Management (2022academic year) Prophase  - その他

  • Environmental Chemistry (2022academic year) Second semester  - 金3~4

  • Environmental Microbiology (2022academic year) Fourth semester  - 水8~9

  • Environmental Physical Chemistry (2022academic year) 1st semester  - 水3~4

  • Environmental physical chemistry A (2022academic year) 1st semester  - 水3~4

  • Environmental physical chemistry B (2022academic year) Second semester  - 金3~4

  • Foundation of environmental sanitation A (2022academic year) Summer concentration  - その他8~9

  • Experiments on environmental sanitation (2022academic year) Fourth semester  - 火1~4

  • Experiments on environmental sanitation (2022academic year) Third semester  - 木5~8

  • Environmental engineering mathematics IA (2022academic year) Fourth semester  - 水5~6

  • Environmental engineering mathematics IA (2022academic year) Second semester  - 金1~2

  • Environmental engineering mathematics IB (2022academic year) Fourth semester  - 水5~6

  • Environmental engineering mathematics IB (2022academic year) Second semester  - 金1~2

  • Civil Engineering I (2021academic year) 1st semester  - 木2,木3

  • Civil Engineering II (2021academic year) Second semester  - 金3,金4

  • Water Supply and Waste Water Treatment (2021academic year) 3rd and 4th semester  - その他

  • Wastewater engineering (2021academic year) Fourth semester  - その他

  • Civil Engineering I (2021academic year) 1st semester  - 木2~3

  • Civil Engineering II (2021academic year) Second semester  - 金3~4

  • System of Sustainable Society (2021academic year) 3rd and 4th semester  - [第3学期]火8~9, [第4学期]木7~8

  • Experimental in Water Quality (2021academic year) Third semester  - 月5~8

  • Experimental in Water Quality (2021academic year) Fourth semester  - 火1~4

  • Water Treatment Engineering (2021academic year) Prophase  - 火5~6

  • Advanced Course on Water Treatment Engineering (2021academic year) Prophase  - その他

  • Water Quality (2021academic year) 1st and 2nd semester  - [第1学期]月3~4, [第2学期]木1~2

  • Water Quality A (2021academic year) 1st semester  - 月3~4

  • Seminar in Water Environment and Sanitation (2021academic year) Prophase  - その他

  • Seminar in Water Environment and Sanitation (2021academic year) Late  - その他

  • Seminar in Water Environment and Sanitation (2021academic year) Late  - その他

  • Seminar in Water Environment and Sanitation (2021academic year) Prophase  - その他

  • Water supply engineering (2021academic year) Third semester  - その他

  • Water supply engineering (2021academic year) Third semester  - その他

  • Special Research (2021academic year) Year-round  - その他

  • Introduction to Environmental & Civil Engineering A (2021academic year) special  - その他

  • Introduction to Environmental & Civil Engineering B (2021academic year) special  - その他

  • Seminar on Environmental Management (2021academic year) Prophase  - その他

  • Seminar in Environmental Management (2021academic year) Late  - その他

  • Seminar on Environmental Management (2021academic year) Late  - その他

  • Seminar in Environmental Management (2021academic year) Prophase  - その他

  • Basic of Architecture, Civil Engineering and Environmental Management (2021academic year) 1st semester  - 水1~2

  • Environmental Chemistry (2021academic year) Second semester  - 金3,金4

  • Environmental Microbiology (2021academic year) Third semester  - その他

  • Environmental Microbiology (2021academic year) Third semester  - その他

  • Environmental Physical Chemistry (2021academic year) 1st semester  - 水3,水4

  • Environmental physical chemistry (2021academic year) 1st and 2nd semester  - [第1学期]その他, [第2学期]金3~4

  • Environmental physical chemistry A (2021academic year) 1st semester  - 水3~4

  • Environmental physical chemistry B (2021academic year) Second semester  - その他

  • Foundation of environmental sanitation A (2021academic year) Third semester  - 火8~9

  • Experiments on environmental sanitation (2021academic year) Third semester  - 月5~8

  • Experiments on environmental sanitation (2021academic year) Fourth semester  - 火1~4

  • Environmental engineering mathematics I (2021academic year) 3rd and 4th semester  - 月8~9

  • Environmental engineering mathematics IA (2021academic year) Third semester  - 月8~9

  • Environmental engineering mathematics IA (2021academic year) Fourth semester  - 月8~9

  • Environmental engineering mathematics IB (2021academic year) Third semester  - 月8~9

  • Environmental engineering mathematics IB (2021academic year) Fourth semester  - 月8~9

  • Civil Engineering I (2020academic year) 1st semester  - 木2,木3

  • Civil Engineering II (2020academic year) Second semester  - 金3,金4

  • Water Supply and Waste Water Treatment (2020academic year) 2nd and 3rd semester  - 木4,木5

  • Wastewater engineering (2020academic year) Third semester  - 木4,木5

  • Laboratory Work for Graduation Thesis (2020academic year) 1st-4th semester  - その他

  • Laboratory Work for Graduation Thesis (2020academic year) Other  - その他

  • Laboratory Work for Graduation Thesis (2020academic year) 1st-4th semester  - その他

  • Civil Engineering I (2020academic year) 1st semester  - 木2,木3

  • Civil Engineering II (2020academic year) Second semester  - 金3,金4

  • System of Sustainable Society (2020academic year) 3rd and 4th semester  - [第3学期]木1,木2, [第4学期]水2,水3

  • Experimental in Water Quality (2020academic year) Third semester  - 月1,月2,月3,月4

  • Experimental in Water Quality (2020academic year) Fourth semester  - 火5,火6,火7,火8

  • Water Treatment Engineering (2020academic year) Prophase  - 火4,火5

  • Advanced Course on Water Treatment Engineering (2020academic year) Prophase  - その他

  • Water Quality (2020academic year) 1st and 2nd semester  - [第1学期]木1,木2, [第2学期]月4,月5

  • Water Quality A (2020academic year) 1st semester  - 木1,木2

  • Water supply engineering (2020academic year) Second semester  - 木4,木5

  • Special Research (2020academic year) Year-round  - その他

  • Present Environmental Problems, Science and Technology (2020academic year) Fourth semester  - 木5,木6

  • Internship of Env. and Civil Engineering (2020academic year) special  - その他

  • Internship of Env. and Civil Engineering (2020academic year) special  - その他

  • Seminar on Environmental Management (2020academic year) Prophase  - その他

  • Seminar in Environmental Management (2020academic year) Late  - その他

  • Seminar on Environmental Management (2020academic year) Late  - その他

  • Seminar in Environmental Management (2020academic year) Prophase  - その他

  • Environmental Microbiology (2020academic year) Fourth semester  - 月2,月3

  • Environmental Microbiology (2020academic year) Fourth semester  - 月2,月3

  • Environmental physical chemistry (2020academic year) 1st and 2nd semester  - [第1学期]火7,火8, [第2学期]火1,火2

  • Environmental physical chemistry A (2020academic year) 1st semester  - 火7,火8

  • Environmental physical chemistry B (2020academic year) Second semester  - 火1,火2

  • Foundation of environmental sanitation A (2020academic year) Third semester  - 木1,木2

  • Experiments on environmental sanitation (2020academic year) Third semester  - 月4,月5,月6,月7

  • Experiments on environmental sanitation (2020academic year) Fourth semester  - 火4,火5,火6,火7

  • Environmental engineering mathematics I (2020academic year) 3rd and 4th semester  - [第3学期]火4,火5, [第4学期]火7,火8

  • Environmental engineering mathematics IA (2020academic year) Third semester  - 火4,火5

  • Environmental engineering mathematics IA (2020academic year) Fourth semester  - 火7,火8

  • Environmental engineering mathematics IB (2020academic year) Third semester  - 火4,火5

  • Environmental engineering mathematics IB (2020academic year) Fourth semester  - 火7,火8

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