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dc.contributor.authorFatimah, Siti
dc.contributor.authorSuyata, Suyata
dc.contributor.authorSetyaningtyas, Tien
dc.date.accessioned2016-02-24T04:40:56Z
dc.date.available2016-02-24T04:40:56Z
dc.date.issued2016-02
dc.identifier.citationAbadulla, E.T. Tzanov, Costa.2000.Decolourization and Detoxification of Textile Dyes with A Loccase from Trametes Hirruta. Applied Environmental Microbiology. 66(8), 3357-3362 Ariana. 1993. Pengolahan Limbah Uranium. No.4. Tabloid STTL. Yogyakarta Culp, R.L.1978. Hand Book of Advanture Waste Water Treatment. Second edition. Litton Educational Publishing Inc. USA Darjito. 2000. Kajian Pengaruh pH Dalam Pembuatan Sol Magnetit Adsorben Logam. Jurnal Ilmu Teknik (Enginering). 12(2) Daneshvar, N., Khataee, A. R., & Djafarzadeh, N. (2006). The use of artificial neural networks (ANN) for modeling of decolorization of textile dye solution containing CI Basic Yellow 28 by electrocoagulation process. Journal of hazardous materials, 137(3), 1788-1795. Dogra,S. 1990. Kimia Fisik. UI press. Jakarta E.Ronald dan Walpole. 1995. Ilmu Peluang Dan Statistik Untuk Insinyur Dan Ilmuwan. ITB. Bandung Famila dan Rahmanto. 2000. Jurnal Sains Dan Matematika. 8(1),25-28 Fessenden, R.J Fessenden. 1999. Kimia Organij. Jilid 2. Erlangga. Jakarta Greeanwood, N.1984. Chemistry of Elements. First edition. Pergamon press. Canada House a Barbara. 2001. Dringking Water Chemistry: A Laboratory Mamal. Lewish Publisher. Florida Ibannez, G.J. 1998. Electrochemical Remediation Of The Environment Fundamentals And Microscale Laboratory Experiment. Chem-educ. 75(8),1040-1041 Kasiri, M. B., Modirshahla, N., & Mansouri, H. (2013). Decolorization of organic dye solution by ozonation; Optimization with response surface methodology. International Journal of Industrial Chemistry, 4(1), 1-10. Koeman, J.H. 1992. Pengantar Ilmi Toksikologi. UGM Press. Yogyakarta Kristanto, J Rahmanto. 2000. Laju Dekolorisasi Fenolftalein Sebagai Fungsi Potensial Eksternal. Jurnal Sains Dan Matematika. 12(2), 25-28 Nowlesys. 1989. Condensed Chemical Dictionary. 11th edition. Van Nostrand Reinhold Company. New York Pala, A..Tokat. and H. Erkayu. 2003. Removal of Some Reactive Dyes From Textile Processing Wastewater Using Powdered Activated Carbon. Proceeding of The First International Conference on Environmental Research and Assasment. Bucharest, Rumania Petrucci. 1989. Kimia Dasar Untuk Universitas. Gramedia. Jakarta Rahmanto, T.H.2000. LAju Elektrodekolorisasi Fenolftalein Sebagai Fungsi Voltase Dua Waktu. Jurnal Sains Dan Matematika, 8(2), 55-58 Robinson. 2001. Remediation of Dyes in Textile Effluent : A Critical Review on Current Treatment Technologies with A Proposed alternative. Bioresource Technology, 77, 247-255 Rivai Harizul. 1995. Asas Pemeriksaan Kimia. UI Pers. Jakarta Sudjana. 2002. Metode Statistik. Tarsito. Bandung Wulfsberg, G. 1989, Principle Of Description Inorganic Chemistry. University Science Book Sausalito. California Yoo, E.S., 2000. Biological and Chemical Mechanism of Reductive Decolourization of Azo Dyes. Disertation Technischen Universital. Berlinin_ID
dc.identifier.issn2407-9189
dc.identifier.urihttp://hdl.handle.net/11617/6682
dc.description.abstractResearch on electrodecolorization of dye rhodamine B has done. The dye rodamin B is one kind of various components in the liquid waste textiles, especially in the dyeing process, Use of the dye rodamin B reaches approximately 60% to 70% and 10% to 15 % lost in the dyeing process. The aim of this study is to provide an alternative method for dealing with liquid wastewater. The method in this study is experimentally to test the qualitative and quantitative test. This study used an electrolysis process in which iron is used as a carbon anode and cathode. Iron anode electrolysis cells will form a metal hydroxide that acts as a coagulant so that the dye can be exempt from a mixture of origin. The first step in this research was to determine the optimum time and the optimum voltage. Conditions that shew the greatest percentage decolorization used in this study. Voltage used is 12V while the optimum use of time is 5 minutes. The results showed that at pH 3, 4, and 6 percentage decolorization relatively close to 100% than at pH 9 and 10. This indicates that the maximum decolorization percentage acidic conditions, because the atmosphere in the case of acid neutralization negative charge of hydroxide ions by hydrogen ions so as to assist the binding molecule H2O2 rodamin B. In addition to the concentration of 300 mg / L occur decolorization greater than without the addition of H2O2in_ID
dc.language.isoidin_ID
dc.publisherLPPM STIKES Muhammadiyah Kudusin_ID
dc.subjectElectrodecolorizationin_ID
dc.subjectRhodamin Bin_ID
dc.subjectelectrolysis Hydrogen peroxidein_ID
dc.titleOptimasi Ph dan Hidrogen Peroksida pada Proses Elektrodekolorisasi Rodamin Bin_ID
dc.typeArticlein_ID


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