Dergiler / International Journal of Agriculture Forestry and Life Sciences / 2020 / Cilt: 4 - Sayı: 1

Obtaining activated carbon from grape pulp and removing of reactive blue 19 from the aqueous solution

Sayfa
62–70
Yayın Tarihi
2020-06-23
DOI
—
🏛️Bu makalenin bibliyografik verileri ve tam metin bağlantısı DergiPark üzerinden sağlanmıştır.
DergiPark Kaydı ↗
✨

Yapay Zeka Hızlı Bakış & Çıkarımlar

AI Insight
⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

The adsorption test results were found to be important in terms of environmental friendliness, economical and easy availability by the activated carbon obtained from the reactive blue 19 textile dye grape pulp.

📌 3 Maddede Bu Makale

🎯
Amaç & Hipotez:As an adsorbent for the removal of reactive blue 19 (RM 19) from the aqueous solution, grape pulp carbon (GMC), an agriculture allow cost by product, was used.
📊
Temel Bulgular & Veri:The surface area of the grape pulp carbon was calculated as 1542.71 m2/g surface area using the BET method.
💡
Sonuç & Katkı:The adsorption test results were found to be important in terms of environmental friendliness, economical and easy availability by the activated carbon obtained from the reactive blue 19 textile dye grape pulp.
🔬Tür:Modelleme & Sayısal Simülasyon
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Grape pulp · chemical activation · activated carbon

Abstract

As an adsorbent for the removal of reactive blue 19 (RM 19) from the aqueous solution, grape pulp carbon (GMC), an agriculture allow cost by product, was used. Activated carbon was obtained by chemical activation of a grape meal with zincchloride. The surface area of the grape pulp carbon was calculated as 1542.71 m2/g surface area using the BET method. The experiment data showed that adsorption was extremely pH dependent and optimal pH was decisived as 3.0. The maximum dye adsorption capacity was 587.7 mg/g at 45 °C. Freundlich and Langmuira adsorption models were used for a mathematical definition of adsorption equilibrium. According to the experimental data, the Freundlich model was a very good fit. Mass transfer and kinetic models were applied to experimental data to investigate the mechanisms of adsorption and potential rate steps. The mass transfer and intraparticle diffusion were found to play an significant role in the adsorption mechanisms of paint and adsorption kinetics in the first-class kinetic model. The adsorption test results were found to be important in terms of environmental friendliness, economical and easy availability by the activated carbon obtained from the reactive blue 19 textile dye grape pulp.

🔖

Bu Makaleye Atıf Yap

GEZER, B. (2020). Obtaining activated carbon from grape pulp and removing of reactive blue 19 from the aqueous solution. International Journal of Agriculture Forestry and Life Sciences, Cilt: 4 - Sayı: 1, 62–70. https://ajindex.com/articles/765484

📄 Tam Metin PDF Okuyucu

📄

PDF görüntüleyici hazırlanıyor...

Kaynakça (1)

  1. Referans1 Ahmad, M.A., Puad, N.A.A., Bello, O.S. (2014). Kinetic, equilibrium and thermodynamic studies of synthetic dye removal using pomegranatepe elactivated carbon prepared by microwave-induced KOH activation. Water Resource Industry, 6, 18–35. Referans2 Akar, T., Celik, S., Akar, S.T. (2010). Biosorption performance of surface modified biomass obtained from Pyracantha coccinea for the decolorization of dye contaminated solutions. Chemistry Engineering Journal, 160, 466–472. Referans3 Ali, I., Gupta, V.K. (2007). Advances in water treatment by adsorption technology. Nature Protocols, 1, 2661–2667. Referans4 Alkan, M., Doğan, M., Turhan, Y., Demirbas, O.,Turan, P. (2008). Adsorption kinetics and mechanism of maxilon Blue 5G dye on sepiolite from aqueous solutions. Chemistry Engineering Journal, 139, 213–223. Referans5 Altundogan, H.S. (2005). Cr(VI) removal from aqueous solution by iron (III) hydroxide loaded sugar beet pulp. Process Biochemistry, 40, 1443–1452. Referans6 Asgher, M. (2012). Biosorpiton of reactive dyes: a review. Water Air Soil Pollution, 223, 2417–2435. Referans7 Ayed, L., Chaieb, K., Cheref, A., Bakhrouf, A. (2010). Biodegradation and decolorization of triphenylmethane dyes by Staphylococcus epidermidis. Desalination, 260, 137-146. Referans8 Baseri, J.R., Palanisamy, P.N., Kumar, P.S. (2012). Adsorption of basic dye from synthetic textile effluent by activated carbon prepared from Thevetiaperuviana. Indian Journal Chemistry Technology, 19, 311–321. Referans9 Bharathi, K.S., Ramesh, S.T. (2013). Removal of dyes using agricultural wastea slow cost adsorbents: a review. Apply Water Science, 3, 773–790. Referans10 Clarke, E.A., Anliker, R. (1980). Organic Dyes and Pigments Handbook of Environmental Chemistry. Anthropogenic Compounds, 3, 181-215. Referans11 Couglin, R.W., Ezra, F.S. (1968). Role of surface acidity in the adsorption of organic pollutants on the surface of carbon. Environment Science Technology, 2, 291-297. Referans12 Dursun, G.,¸ İcek, H.C., Dursun, A.Y. (2005). Adsorption of phenol from aqueous solution by using carbonized beet pulp. Journal Hazardous Materials, 125, 175–182. Referans13 Farah, J.Y., El-Gendy, N.S., Farahat, L.A. (2007). Biosorption of Astrazone Blue basic dye from an aqueous solution using dried biomass of Baker’s yeast. Journal Hazardous Materials, 148, 402–408. Referans14 Faria, P.C.C., Órfão, J.J.M., Pereira, M.F.R. (2004). Adsorption of anionic and cationic dyes on activated carbons with different surf