Adsorption of Remazol Brilliant Blue R Dye Using Activated Carbon from Emty Palm Oil Bunches

Adsorption of Remazol Brilliant Blue R Dye Using Activated Carbon from Emty Palm Oil Bunches

Authors

  • Denny Aris Setiawan Polnes
  • Sirajuddin Politeknik Negeri Samarinda
  • Ricky Marthin De Tulus Wanwol

DOI:

https://doi.org/10.31938/jsn.v13i4.527

Keywords:

Adsorption, adsorbent, Empty palm fruit bunches, dye, Remazol Brilliant Blue R

Abstract

Various types of dyes are used in the textile industry, including Remazol Brilliant Blue R dye. Remazol dye is a type of anthraquinone which is very difficult to remove if it is contaminated in the environment. One method of dealing with dyes that pollute the environment is adsorption using activated carbon. The material for activated carbon has the most potential to come from the palm oil industry, namely empty palm fruit bunches because they are widely available and have economic value. This study aimed to determine the effect of varying exposure time between activated carbon made from empty palm fruit bunches and textile dye Remazol Brilliant Blue R on decreasing the concentration of dye Remazol Brilliant Blue R. The adsorption process was carried out with the ratio of adsorbent mass: dye volume w/v (0.1:15) and varying the contact times of 20, 40, 60, 80, 100 and 120 minutes. The initial concentration of textile substances was 23.2121 mg/L and was contacted between Remazol Brilliant Blue R textile substances with adsorbents using a shaker. Analysis of adsorption results using a UV – Vis instrument with a wavelength of 670 nm for Remazol Brilliant Blue R dye. The results showed that the best adsorption conditions was 60 minute contact time, with a removal percentage of 87.23% with an adsorption capacity of 3.0373 mg/g. The adsorption of Remazol Brilliant Blue R follows the Langmuir adsorption equation model with an R2 of 0.9997.

Downloads

Download data is not yet available.

References

Agustina, L., Udiantoro, & Halim, A. (2016). Karakteristik Serat Tandan Kosong Kelapa Sawit (Tkks) Dengan Empty Fruit Bunches (Efb) Fiber With Boiling And Steaming Treatment). Ziraa’Ah, 41(1), 97–102.

Asnawati, A. (2017). Penentuan Kapasitas Adsorpsi Selulosa Terhadap Rhodamin B dalam Sistem Dinamis. Jurnal Kimia Riset, 2(1), 23. https://doi.org/10.20473/jkr.v2i1.3553

Bahmid, N. A. (2014). Pengembangan Nanofiber selulosa asetat dari selulosa tandan kosong kelapa sawit untuk pembuatan bioplastik [Institut Pertanian Bogor]. In Implementation Science (Vol. 39, Issue 1).

Çatl?oglu, F., Akay, S., Turunç, E., Belgin, G., Anastopoulos, I., Kayan, B., & Kalderis, D. (2021). Environmental Nanotechnology , Monitoring & Management Preparation and application of Fe-modified banana peel in the adsorption of methylene blue : Process optimization using response surface methodology. Environmental Nanotechnology, Monitoring & Management, 16(June).

Firdaus, Y. (2011). Dekolorisasi Zat Warna Remazol Brilliant Blue Menggunakan Membran Padat Silika.

Gova, M. A., & Oktasari, A. (2019). Arang Aktif Tandan Kosong Kelapa Sawit Sebagai Adsorben Logam Berat Merkuri (Hg). In Prosiding Seminar Nasional Sains Dan Teknologi, 2(1), 1–14.

Haryono, H., Faizal D, M., Liamita N, C., & Rostika, A. (2018). Pengolahan Limbah Zat Warna Tekstil Terdispersi dengan Metode Elektroflotasi. EduChemia (Jurnal Kimia Dan Pendidikan), 3(1), 94. https://doi.org/10.30870/educhemia.v3i1.2625

Hidayati, P., Ulfin, I., & Juwono, H. (2016). Adsorption of Remazol Brilliant Blue R, Using Nata de coco: Dosage Optimization. Jurnal Sains Dan Seni ITS, 5(2), 134–136. https://doi.org/http://dx.doi.org/10.12962/j23373520.v5i2.18153

Khuluk, rifki husnul. (2016). Karbon Aktif Dari Tempurung Kelapa ( Cocous nucifera L .) Sebagai Adsorben Zat Warna Metilen Blue. Ii, 1–66.

Maslahat, M., Arissujaya, D., & Lismayani, S. (2018). Optimasi Suhu Aktivasi Pada Pembuatan Arang Aktif Berbahan Dasar Limbah Tandan Kosong Kelapa Sawit. Prosiding Seminar Lignoselulosa 2018, September, 46–51.

Pandiarajan, A., Kamaraj, R., & Vasudevan, S. (2018). Bioresource Technology OPAC ( orange peel activated carbon ) derived from waste orange peel for the adsorption of chlorophenoxyacetic acid herbicides from water : Adsorption isotherm , kinetic modelling and thermodynamic studies. Bioresource Technology, 261(January), 329–341.

Sanada, R. A. (2014). Adsorpsi zat warna kationik (methylene blue) menggunakan karbon aktif tempurung kelapa dan batu bara serta efisiensi regenerasinya= Adsorption of cationic dye methylene blue using coconut shell and coal based activated carbon and its regeneration efficien. Envriomental Engineering.

Sari, M. F. P., Loekitowati, P., & Mohadi, R. (2017). Penggunaan Karbon Aktif Dari Ampas Tebu Sebagai Adsorben Zat Warna Procion Merah Limbah Cair Industri Songket. Journal of Natural Resources and Environmental Management, 7(1), 37–40.

Statistik, B. P. (2022). Produksi Tanaman Perkebunan. Badan Pusat Statistik. https://www.bps.go.id/indicator/54/132/1/produksi-tanaman-perkebunan.html

Sukarta, I. N., Kadek, N., & Lusiani, S. (2016). Adsorpsi Zat Warna Azo Jenis Remazol Brilliant Blue Oleh Limbah Daun Ketapang ( Terminalia Catappa . L .). 311–316.

Downloads

Published

2023-11-13

How to Cite

Setiawan, D. A., Sirajuddin, & Ricky Marthin De Tulus Wanwol. (2023). Adsorption of Remazol Brilliant Blue R Dye Using Activated Carbon from Emty Palm Oil Bunches. JURNAL SAINS NATURAL, 13(4), 183–190. https://doi.org/10.31938/jsn.v13i4.527

Metrics

Loading...