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Journal articles on the topic 'Reactive orange 16'

Author: Grafiati

Published: 4 June 2021

Last updated: 25 July 2025

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1

Dr., P. PARIMALA DEVI. "REMOVAL OF REACTIVE ORANGE 16 FROM AQUEOUS SOLUTIONS BY ADSORPTION ONTO ACTIVATED CARBONS PREPARED FROM WASTE COCONUT FLOWERS." International Journal of Mathematics and Physical Sciences Research 12, no. 2 (2025): 37–44. https://doi.org/10.5281/zenodo.14604664.

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<strong>Abstract:</strong> Coconut tree flowers waste was investigated as a low-cost and effective adsorbent for the adsorption of Reactive Orange 16 from aqueous solution. Physico - Chemical characteristics of the adsorbents were studied as per the standard testing methods. Effect of various parameters such as agitation time, adsorbent dose and concentration, pH, temperature have been investigated in the present study. The adsorption of dyes have been best described by pseudo second order kinetic model and Langmuir adsorption Isotherms. The negative values of the   ∆Gº and posi

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2

Milanovic, Predrag, Marija Vuksanovic, Miodrag Mitric, Aleksandar Kojovic, Dusan Mijin, and Radmila Jancic-Hainemann. "Alumina particles doped with ferric as efficient adsorbent for removal of Reactive Orange 16 from aqueous solutions." Science of Sintering 50, no. 4 (2018): 467–76. http://dx.doi.org/10.2298/sos1804467m.

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Ferric oxide doped alumina particles were prepared via the sol-gel method and their performance as Reactive Orange 16 adsorbent was evaluated. The concentrations of the Reactive Orange 16 were monitored using a UV-Vis spectrophotometer. The effect of Reactive Orange 16 concentration, adsorbent quantity and pH on the solution decolorization efficiency was analyzed. The efficiency of the Reactive Orange 16 removal using ferric oxide alumina doped exceeded 98 % in 20 min at pH=3. The experimental data were fitted to the Langmuir equation better than to the Freundlich one. The pseudo-first-order m

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3

Mitrović, Jelena, Miljana Radović-Vučić, Miloš Kostić, et al. "The effect of anions on decolorization of textile azo dye Reactive Orange 16 with UV/H2O2 process." Advanced Technologies 8, no. 1 (2019): 33–40. http://dx.doi.org/10.5937/savteh1901033m.

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4

Filipkowska, Urszula, Joanna Rodziewicz, Mirosław Krzemieniewski, and Ewa Dłuska. "The Removal of C.I. Reactive Black 8 and Reactive Orange 16 by Ozonation." Polish Journal of Natural Science 23, no. 3 (2008): 659–66. http://dx.doi.org/10.2478/v10020-008-0052-9.

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5

Akbaş, Halide, and Çiğdem Kartal. "C.I. Reactive Orange 16-dodecylpyridinium chloride interactions in electrolytic solutions." Spectrochimica Acta Part A: Molecular and Biomolecular Spectroscopy 65, no. 1 (2006): 95–99. http://dx.doi.org/10.1016/j.saa.2005.09.033.

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6

Chen, Chih-Yu. "Photocatalytic Degradation of Azo Dye Reactive Orange 16 by TiO2." Water, Air, and Soil Pollution 202, no. 1-4 (2009): 335–42. http://dx.doi.org/10.1007/s11270-009-9980-4.

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7

Šíma, J., J. Pocedič, and P. Hasal. "Decolorization of Reactive Orange 16 in Rotating Drum Biological Contactor." Journal of Environmental Chemical Engineering 4, no. 4 (2016): 4540–48. http://dx.doi.org/10.1016/j.jece.2016.10.010.

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8

Mijin, Dusan, Dragana Zlatic, Gordana Uscumlic, and Petar Jovancic. "Solvent effects on photodegradation of CI Reactive Orange 16 by simulated solar light." Chemical Industry 62, no. 5 (2008): 275–81. http://dx.doi.org/10.2298/hemind0805275m.

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Organic solvents may appear in wastewaters and other industrial waste streams containing dyes, therefore, their photodegradation catalyzed by TiO2 should be investigated. Solvent effect on photodegradation of CI Reactive Orange 16 has been studied using simulated solar light and P-25 TiO2. Methyl, ethyl and isopropyl alcohol as well as acetone were used as solvents. Photodegradation reaction was faster in methyl than in ethyl alcohol while in water was the slowest. RO16 photodegradation efficiency and reaction rate decreased in the presence of small concentration of ethanol. Higher photodegrad

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9

Mijin, Dusan, Vuk Tomic, and Branimir Grgur. "Electrochemical decolorization of the reactive orange 16 dye using dimensionally stable Ti/PtOx anode." Journal of the Serbian Chemical Society 80, no. 7 (2015): 903–15. http://dx.doi.org/10.2298/jsc140917107m.

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Electrochemical decolorization of the Reactive Orange 16 was studied using dimensionally stable Ti/PtOx anode in the chloride containing solution. Different reaction parameters, agitation speed, applied current, sodium chloride concentration, and dye concentration was varied and optimum electrolysis conditions were suggested. The hypohlorous acid was suggested to be an active species in the electrochemical decolorization. Reaction was also studied using UV-Vis spectrophotometry, high-pressure liquid chromatography (HPLC), and total organic carbon (TOC) and total nitrogen (TN) analyses.

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10

Ruscasso, F., I. Cavello, M. Butler, E. Lopez Loveira, G. Curutchet, and S. Cavalitto. "Biodegradation and detoxification of reactive orange 16 by Candida sake 41E." Bioresource Technology Reports 15 (September 2021): 100726. http://dx.doi.org/10.1016/j.biteb.2021.100726.

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11

Won, S. W., S. B. Choi, B. W. Chung, D. Park, J. M. Park, and Y. S. Yun. "Biosorptive Decolorization of Reactive Orange 16 Using the Waste Biomass ofCorynebacteriumglutamicum." Industrial & Engineering Chemistry Research 43, no. 24 (2004): 7865–69. http://dx.doi.org/10.1021/ie049559o.

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12

Khan, Mohammad Zain, Satyendra Singh, T. R. Sreekrishnan, and S. Z. Ahammad. "Feasibility study on anaerobic biodegradation of azo dye reactive orange 16." RSC Adv. 4, no. 87 (2014): 46851–59. http://dx.doi.org/10.1039/c4ra06716a.

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Higher colour removal (>90%) shows feasibility of azo dye degradation by anaerobic digestion. Hydrogenotrophic methanogens are the key methane producers. Long retention time is useful for degrading aromatic amines under anaerobic condition.

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13

Syahmi, Mohamad Adib, and Fazilah Ariffin. "Biodegradation of Synthetic Reactive Orange 16 Dye in Anaerobic Reactor Conditions." Journal of Biochemistry, Microbiology and Biotechnology 11, no. 1 (2023): 66–70. http://dx.doi.org/10.54987/jobimb.v11i1.815.

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Industrial use of azo dyes has been linked to severe environmental damage in the textile and apparel sectors. The breakdown products of many azo dyes are poisonous and mutagenic, posing a threat to human health and the environment. Hence, azo dye wastewater bioremediation is gaining interest. The objective of this study was focused on the biodegradation of an azo dye, Reactive Orange 16 (RO16), in an anaerobic continuous tank reactor operated with digested sludge sample. The digested sludge was used as the organic biodegradation agent for azo dye. The aim was to investigate the fate of the ana

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14

Moradi, Ebrahim1 Doleh Mohammad2 Porbahri zahra3and Zazouli Mohammad Ali. "Biosorption Reactive Orange 16 Dye from the Aqueous Environments by Brown seaweed Sargassum glaucescens." International Journal of Advanced Biotechnology and Research 13, no. 1 (2022): 20–28. https://doi.org/10.5281/zenodo.6283589.

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<strong>Background and purpose:</strong> Dyes are oneof the most important environmental pollutants in industrial wastewaters. Due to the complex molecular structure, toxic removal of the pollutant is always challenging. This study aimed to evaluate the efficiency of Sargassum glaucescens in the adsorption of ReactiveOrange16 dyein aquatic environments. <strong>Materials and Methods:</strong> This research was a lab study. S. glaucescens was used as an adsorbent to remove dye Reactive Orange 16. The effect of various parameters such as pH, initial dyes concentration, adsorbent dose, contact ti

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15

Fifi Nurfiana, Rochmadi Rochmadi, Rochim Bakti Cahyono, Hendig Winarno, Sugili Putra, and Waringin M. Yusmaman. "DEGRADATION KINETICS OF TEXTILE AZO DYE REACTIVE ORANGE-16 BY GAMMA IRRADIATION." Jurnal Teknologi (Sciences & Engineering) 86, no. 6 (2024): 131–39. http://dx.doi.org/10.11113/jurnalteknologi.v86.21973.

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Gamma radiation have become attention since their high potential for degrading compounds, especially organic pollutants. In this research, gamma radiation was studied for degrading the Reactive Orange-16 (RO-16) dye, a toxic and carcinogenic pollutant. The radiolytic degradation process was studied in a batch reactor with a gamma-ray dose rate of 2.930 kGy/h. The effect of experimental variable such as initial peroxide concentration, initial pH, initial dye concentration, and addition of inorganic anion were studied. The highest degradation rates were achieved at a peroxide concentration rangi

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16

Yildirim, Ayfer. "Removal of the Anionic Dye Reactive Orange 16 by Chitosan/Tripolyphosphate/Mushroom." Chemical Engineering & Technology 44, no. 8 (2021): 1371–81. http://dx.doi.org/10.1002/ceat.202100077.

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17

Mitrovic, Jelena, Miljana Radovic, Danijela Bojic, Tatjana Andjelkovic, Milovan Purenovic, and Aleksandar Bojic. "Decolorization of textile azo dye reactive orange 16 with UV/H2O2 process." Journal of the Serbian Chemical Society 77, no. 4 (2012): 465–81. http://dx.doi.org/10.2298/jsc110216187m.

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The photochemical decolorization of C.I. Reactive Orange 16 (RO16), a reactive textile azo dye by the UV/H2O2 process using a batch photoreactor with UV lamps emitting at 253.7 nm, was studied. Complete decolorization of 50.0 mg dm-3 initial dye concentration was achieved in less than 6 min under optimal conditions (25 mM initial peroxide concentration, at pH 7.0 and with UV light intensity 1950 ?W cm-2). The effect of experimental variables, such as initial pH, initial concentration of H2O2, initial dye concentration, and the intensity of UV light was studied. The highest decolorization rates

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18

Puasa, S. W., M. S. Ruzitah, and A. S. A. K. Sharifah. "Simplified Colorimetric Method Using Reactive Orange 16 for Analysis of Cationic Surfactant." Advanced Materials Research 701 (May 2013): 342–46. http://dx.doi.org/10.4028/www.scientific.net/amr.701.342.

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The concentration of surfactant is usually determined by a colorimetric method. A simplified colorimetric method for determining cationic surfactant was proposed which has advantages over the existing colorimetric method where less chemical is used and the overall time to perform the analysis per sample is reduced by half. These methods were tested based on analyzing the ionic interaction of cationic surfactant-reactive orange 16 (PBE-RO16) mixtures. A linear correlation was observed between the absorbance ratio of PBE-RO16 mixture/dye and PBE concentration. Results obtained from this study sh

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19

Gomes, Luciano, Douglas W. Miwa, Geoffroy R. P. Malpass, and Artur J. Motheo. "Electrochemical degradation of the dye reactive orange 16 using electrochemical flow-cell." Journal of the Brazilian Chemical Society 22, no. 7 (2011): 1299–306. http://dx.doi.org/10.1590/s0103-50532011000700015.

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20

ŞAHİNKAYA, Serkan. "Decolorization of reactive orange 16 via ferrate(VI) oxidation assisted by sonication." TURKISH JOURNAL OF CHEMISTRY 41 (2017): 577–86. http://dx.doi.org/10.3906/kim-1701-8.

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21

El Aggadi, Sanaa, Nidae Loudiyi, Aicha Chadil, Omar Cherkaoui, and Abderrahim El Hourch. "Electrochemical oxidation of textile azo dye reactive orange 16 on the Platinum electrode." Mediterranean Journal of Chemistry 10, no. 1 (2020): 82–89. http://dx.doi.org/10.13171/mjc10102001311108sea.

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This study focused mainly on the color removal of textile azo dye Reactive Orange 16 (RO16) by electrochemical oxidation. The effect of supporting electrolyte (H2SO4 and NaOH), RO16 concentration (from 0.5 to 10 mM) and potential scan rate (between 20 and 500 mV/s) was performed with cyclic voltammetry using platinum (Pt) wire as working electrode. The anodic peak current density was linear to RO16 concentrations. This allows the lowest concentrations to be determined voltammetrically in the two electrolytic media, acid (H2SO4 1 M) and alkaline (NaOH 0.1 M). Linearity between the current densi

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22

Pereira, Valeen Rashmi, Arun M. Isloor, A. K. Zulhairun, M. N. Subramaniam, W. J. Lau, and A. F. Ismail. "Preparation of polysulfone-based PANI–TiO2 nanocomposite hollow fiber membranes for industrial dye rejection applications." RSC Advances 6, no. 102 (2016): 99764–73. http://dx.doi.org/10.1039/c6ra18682c.

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Polysulfone-based nano-polyaniline–TiO<sub>2</sub> containing hollow fiber membranes were prepared via a dry wet spinning method. The membranes were used for rejection of Reactive Black-5 and Reactive Orange-16 dyes.

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23

Suteu, Daniela, Carmen Zaharia, and Teodor Malutan. "Removal of orange 16 reactive dye from aqueous solutions by waste sunflower seed shells." Journal of the Serbian Chemical Society 76, no. 4 (2011): 607–24. http://dx.doi.org/10.2298/jsc100721051s.

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In this work, the use of an agro-industrial waste, i.e., sunflower seed shells, was investigated as a sorbent for the removal of Orange 16 reactive dye from aqueous environments. Batch experiments were performed as a function of pH, sorbent dose, dye concentration, temperature and contact time. The percent dye removal increased with increasing sorbent dose and temperature of the aqueous solution, and decreased with increasing dye concentration; the required contact time was five hours. The Freundlich, Langmuir, Dubinin-Radushkevich and Tempkin adsorption isotherms were used to describe the equ

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24

Sultana, Saima, Mohammad Danish Khan, Suhail Sabir, Khalid M. Gani, Mohammad Oves, and Mohammad Zain Khan. "Bio-electro degradation of azo-dye in a combined anaerobic–aerobic process along with energy recovery." New Journal of Chemistry 39, no. 12 (2015): 9461–70. http://dx.doi.org/10.1039/c5nj01610j.

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25

Zakaria, Zuhailie, Mohamed Rozali Othman, Siti Zubaidah Hasan, and Wan Yaacob Wan Ahmad. "Electrochemical Degradation of Reactive Orange 16 by using Charcoal-Based Metallic Composite Electrodes." Sains Malaysiana 48, no. 4 (2019): 791–801. http://dx.doi.org/10.17576/jsm-2019-4804-11.

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26

Ravindiran, Gokulan, Kalyani Gaddam, and Killi Sunil. "Experimental Investigation on Reactive Orange 16 Removal Using Waste Biomass of Ulva prolifera." Advances in Materials Science and Engineering 2022 (May 23, 2022): 1–8. http://dx.doi.org/10.1155/2022/7323588.

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Ulva prolifera marine seaweed was tested for its capacity to eliminate reactive orange 16 (RO16) from aqueous solutions. Algae has recently been regarded as one of the most environmental friendly wastewater treatment methods and resources. The batch study used variations in solution pH, sorbent dosage, initial dye concentration, and temperature. The biochar was characterized using Fourier transform infrared (FT-IR) spectroscopy, an elemental analyser, proximate analysis, and a BET analyser. The adsorption mechanism was further investigated using adsorption isotherm and kinetic models. The ther

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27

Akbaş, Halide, and Tanzer Taner. "Spectroscopic studies of interactions between C.I. Reactive Orange 16 with alkyltrimethylammonium bromide surfactants." Spectrochimica Acta Part A: Molecular and Biomolecular Spectroscopy 73, no. 1 (2009): 150–53. http://dx.doi.org/10.1016/j.saa.2009.02.018.

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28

Chittal, Vaibhavi, Magaly Gracias, Anagha Anu, Purbasha Saha, and K. V. Bhaskara Rao. "Biodecolorization and Biodegradation of Azo Dye Reactive Orange-16 by Marine Nocardiopsis sp." Iranian Journal of Biotechnology 17, no. 3 (2019): 18–26. http://dx.doi.org/10.29252/ijb.1551.

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29

Mishra, Saurabh, and Abhijit Maiti. "Process optimization for effective bio-decolourization of reactive orange 16 using chemometric methods." Journal of Environmental Science and Health, Part A 54, no. 3 (2018): 179–92. http://dx.doi.org/10.1080/10934529.2018.1541383.

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30

Kim, Jong Lae. "Preparation of Blue-Light Blocking Hydrogel Contact Lenses Using Reactive Orange 16 Dye." Korean Journal of Vision Science 24, no. 4 (2022): 445–52. http://dx.doi.org/10.17337/jmbi.2022.24.4.445.

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31

Svobodová, Kateřina, Marion Senholdt, Čeněk Novotný, and Astrid Rehorek. "Mechanism of Reactive Orange 16 degradation with the white rot fungus Irpex lacteus." Process Biochemistry 42, no. 9 (2007): 1279–84. http://dx.doi.org/10.1016/j.procbio.2007.06.002.

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32

Vijayaraghavan, K., Sung Wook Won, and Yeoung-Sang Yun. "Single- and Dual-Component Biosorption of Reactive Black 5 and Reactive Orange 16 onto Polysulfone-Immobilized EsterifiedCorynebacteriumglutamicum." Industrial & Engineering Chemistry Research 47, no. 9 (2008): 3179–85. http://dx.doi.org/10.1021/ie071537p.

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33

GOTO, SHINPEI, TOSHIYUKI SHIMIZU, and SATOSHI SODA. "Ozonation for Decolorization and Biodegradability Enhancement of Synthetic Wastewater Containing Reactive Black 5 and Reactive Orange 16." Japanese Journal of Water Treatment Biology 59, no. 3 (2023): 33–37. http://dx.doi.org/10.2521/jswtb.59.33.

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34

Rancev, Sasa, Milica Petrovic, Aleksandar Bojic, Dragan Radivojevic, Cedomir Maluckov, and Miodrag Radovic. "Degradation of reactive orange 16 using a prototype atmospheric-pressure non-thermal plasma reactor." Facta universitatis - series: Physics, Chemistry and Technology 16, no. 3 (2018): 285–95. http://dx.doi.org/10.2298/fupct1803285r.

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A prototype atmospheric pressure non-thermal corona plasma reactor system is developed and tested for the removal of commercial textile reactive dye from water. The dye can be completely degraded in water by the presented reactor system in the initial concentration range of 10-100 mg dm-3. Dye degradation rate decreases with the increase of initial dye concentration and pulse frequency. The pH of treated solutions decreases with the increase of treatment time and with the decrease of the applied frequency. Solutions electrical conductivity increases with an increase of treatment time and with

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35

Pramugani, Ahsin, Toshiyuki Shimizu, Shinpei Goto, Teti Armiati Argo, and Satoshi Soda. "Decolorization and Biodegradability Enhancement of Synthetic Batik Wastewater Containing Reactive Black 5 and Reactive Orange 16 by Ozonation." Water 14, no. 20 (2022): 3330. http://dx.doi.org/10.3390/w14203330.

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The batik industry generates large amounts of highly colored wastewater. Azo dyes in batik wastewater can cause environmental pollution. In this study, synthetic batik wastewater containing 32 mg/L Reactive Black 5 (RB5) and 32 mg/L Reactive Orange 16 (RO16) was treated by ozonation in a 2 L batch reactor. The wastewater color unit was reduced from 4240 to 70 after 10 min ozonation and to below 50 after 15 min ozonation (7.3 g O3/m3, 4 L/min). The first-order decay constant for 5 min ozonation was determined to be 1.11 min−1 for RB5 and 0.82 min−1 for RO16. Biodegradation tests using activated

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36

Caliman, Anca Florentina, Apostolis Antoniadis, Ioannis Poulios, and Matei Macoveanu. "KINETIC STUDY ON HETEROGENEOUS PHOTOCATALYTIC DEGRADATION OF REACTIVE ORANGE 16 INTO A SLURRY REACTOR." Environmental Engineering and Management Journal 5, no. 4 (2006): 649–59. http://dx.doi.org/10.30638/eemj.2006.052.

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37

Muralikrishnan, R., and C. Jodhi. "Experimental studies and mathematical modeling of decolorization of Reactive Orange 16 in packed column." DESALINATION AND WATER TREATMENT 217 (2021): 422–30. http://dx.doi.org/10.5004/dwt.2021.26909.

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38

Mohd Nasir, Muhamad Zulhelmie, Muhammad Abbas Ahmad Zaini, and Mohd Aziz Che Yunus. "Adsorption profiles of rhodamine B and reactive orange 16 onto pharmaceutical-based activated charcoals." DESALINATION AND WATER TREATMENT 132 (2018): 340–49. http://dx.doi.org/10.5004/dwt.2018.23152.

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39

Lazarević, Slavica, Vesna Marjanović, Ivona Janković-Častvan, Ljiljana Živković, Djordje Janaćković, and Rada Petrović. "Effective removal of Reactive Orange 16 dye from aqueous solution by amine-functionalized sepiolites." DESALINATION AND WATER TREATMENT 163 (2019): 376–84. http://dx.doi.org/10.5004/dwt.2019.24437.

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40

Patil, Suhas R., U. G. Akpan, and B. H. Hameed. "Photocatalytic activity of sol–gel-derived mesoporous TiO2thin films for reactive orange 16 degradation." Desalination and Water Treatment 53, no. 13 (2013): 3604–14. http://dx.doi.org/10.1080/19443994.2013.872577.

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41

Gunasegaran, Manassvinee, Suganthi Ravi, and Noor Fazliani Shoparwe. "Kinetic Studies of Reactive Orange 16 (RO16) Dye Removal from Aqueous Solution using PIMs." Journal of Physics: Conference Series 1529 (May 2020): 052003. http://dx.doi.org/10.1088/1742-6596/1529/5/052003.

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42

Castañeda Ulloa, Locksley Fabian, Oscar Miguel Cornejo, and José Luis Nava. "Modeling of the Electro-Peroxone Process for the Degradation of Orange Reactive 16 Dye." ECS Transactions 86, no. 4 (2018): 129–38. http://dx.doi.org/10.1149/08604.0129ecst.

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43

Akdogan, Hatice Ardag, and Merve Canpolat. "Removal of reactive orange 16 by immobilized Coprinus plicatilis in the batch shaking bioreactor." Fibers and Polymers 14, no. 1 (2013): 76–81. http://dx.doi.org/10.1007/s12221-013-0076-9.

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44

Tizaoui, Chedly, and Naser Grima. "Kinetics of the ozone oxidation of Reactive Orange 16 azo-dye in aqueous solution." Chemical Engineering Journal 173, no. 2 (2011): 463–73. http://dx.doi.org/10.1016/j.cej.2011.08.014.

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45

Kapdan, Ilgi Karapinar, and Rukiye Oztekin. "Decolorization of textile dyestuff Reactive Orange 16 in fed-batch reactor under anaerobic condition." Enzyme and Microbial Technology 33, no. 2-3 (2003): 231–35. http://dx.doi.org/10.1016/s0141-0229(03)00128-5.

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46

Doondani, Priyanka, Ravin Jugade, Vaishnavi Gomase, Anita Shekhawat, Apurva Bambal, and Sadanand Pandey. "Chitosan/Graphite/Polyvinyl Alcohol Magnetic Hydrogel Microspheres for Decontamination of Reactive Orange 16 Dye." Water 14, no. 21 (2022): 3411. http://dx.doi.org/10.3390/w14213411.

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A rapid gelation method was used to fabricate magnetic chitosan/graphite/polyvinyl alcohol (m-CGPA) hydrogel beads crosslinked with glutaraldehyde. A thorough characterization was carried out by FTIR, SEM-EDX, XRD, VSM, and TGA. Studies with batch experiments indicated that m-CGPA removes more than 95% of reactive orange 16 (RO 16) dye with a Langmuir monolayer adsorption capacity of 196.3 mg/g at pH 4.0 in just 90 min of contact time. Langmuir isotherm model fitted well with the experimental data. Pseudo-second order kinetics was proposed for the adsorption process. Adsorption thermodynamics

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47

Won, Sung Wook, Sun Beom Choi, and Yeoung-Sang Yun. "Performance and mechanism in binding of Reactive Orange 16 to various types of sludge." Biochemical Engineering Journal 28, no. 2 (2006): 208–14. http://dx.doi.org/10.1016/j.bej.2005.11.006.

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48

Ray, SK, P. Saha, HP Nur, D. Saha, AI Hoque, and S. Saha. "Study on the preparation of polymer-grafted coir fibre based adsorbent and its application to remove a reactive dye from aqueous solution." Bangladesh Journal of Scientific and Industrial Research 48, no. 4 (2014): 271–80. http://dx.doi.org/10.3329/bjsir.v48i4.18277.

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Holocellulose was separated from Coir fibre by Sodium chlorite bleaching procedure. The adsorbent was synthesized by graft-copolymerization of acrylamide onto separated cellulose using potassium persulfate as a free radical initiator. Grafting percentage and grafting efficiency were measured and found to be 74.5 and 58% respectively. Prepared adsorbent was characterized by applying Fourier Transform- Infrared Spectrophotometer, Thermogravimetric/Differential Thermal Analyzer and Scanning Electron Microscope. Adsorbent prepared from holocellulose was successfully used at different adsorbent dos

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49

Ariff, M. Mohamad, and M. A. Ahmad Zaini. "CARBON-BASED BETA-CYCLODEXTRIN ADSORBENT FOR METHYLENE BLUE AND REACTIVE ORANGE 16 REMOVAL FROM WATER." ACTA CHEMICA IASI 28, no. 1 (2020): 19–30. http://dx.doi.org/10.2478/achi-2020-0002.

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50

Akbaş, Halide, and Tanzer Taner. "The Effect of Electrolytes on the Interaction of C. I. Reactive Orange 16-Tetradecyltrimethylammonium Bromide." Tenside Surfactants Detergents 50, no. 2 (2013): 84–89. http://dx.doi.org/10.3139/113.110235.

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