To treat or not to treat? Applying chemical engineering tools and a life cycle approach to assessing the level of sustainability of a clean-up technologyElectronic supplementary information (ESI) available: granular activated carbon adsorption. Process design and modelling. See http://www.rsc.org/suppdata/gc/b4/b401871k/

2004 ◽  
Vol 6 (8) ◽  
pp. 395 ◽  
Author(s):  
Omar Romero-Hernandez
Keyword(s):  
Activated Carbon ◽  
Life Cycle ◽  
Process Design ◽  
Chemical Engineering ◽  
Adsorption Process ◽  
Granular Activated Carbon ◽  
Supplementary Information ◽  
Life Cycle Approach ◽  
Activated Carbon Adsorption ◽  
Carbon Adsorption

Granular activated carbon adsorption process for removing trichloroethylene from groundwater

AIChE Journal ◽  
2011 ◽  
Vol 57 (2) ◽  
pp. 542-550 ◽  
Author(s):  
Liuya Huang ◽  
Zhidong Yang ◽  
Bingjing Li ◽  
Juan Hu ◽  
Wei Zhang ◽  
...  
Keyword(s):  
Activated Carbon ◽  
Adsorption Process ◽  
Granular Activated Carbon ◽  
Activated Carbon Adsorption ◽  
Carbon Adsorption

Granular Activated Carbon Adsorption

2005 ◽  
pp. 573-633 ◽  
Author(s):  
Yung-Tse Hung ◽  
Howard H. Lo ◽  
Lawrence K. Wang ◽  
Jerry R. Taricska ◽  
Kathleen Hung Li
Keyword(s):  
Activated Carbon ◽  
Granular Activated Carbon ◽  
Activated Carbon Adsorption ◽  
Carbon Adsorption

Activated Carbon from Sugarcane (Saccharum officinarum L.) Bagasse for Removal Ca2+ and Mg2+ Ion from Well Water

2020 ◽  
Vol 2 (2) ◽  
pp. 22-32
Author(s):  
Ira Tyas Kurniasari ◽  
Cucun Alep Riyanto ◽  
Yohanes Martono
Keyword(s):  
Activated Carbon ◽  
Adsorption Process ◽  
High Hardness ◽  
Saccharum Officinarum ◽  
Well Water ◽  
Activated Carbon Adsorption ◽  
Adsorption Method ◽  
Impregnation Ratio ◽  
Carbon Adsorption ◽  
Stirring Time

Humans need water with good quality to fulfill their needs. Water with high hardness content will have a bad impact if consumed continuously, so the adsorption method is carried out to reduce the concentration of Ca2+ and Mg2+ ions. The adsorption process uses sugarcane bagasse activated carbon (SBAC) and the tested water sample is well water in District Jati, Kudus. Synthesis of  SBAC was conducted with H3PO4 30% as an activator at an impregnation ratio of 1:5 (w/w) at temperature 700°C. The FTIR result showed that SBAC contains O-H, C-H, C=C, C≡C, and C-O as functional groups. Analysis result with the XRD instrument showed that the microstructure of SBAC that is formed is turbostatic structure and amorphous. Modeling isotherm suitable for SBAC adsorption on Ca2+ ions is Langmuir isotherm where the R2 value is 0.9134 which shows that the adsorption process occurs chemically and monolayer. Modeling isotherm suitable for SBAC adsorption on Mg2+ ions is Elovich isotherm where the R2 value is 0.8638 which means that the adsorption process is multilayer and adsorption in non-ideal conditions. Modeling kinetics suitable for SBAC adsorption on  Ca2+ and Mg2+ ions is Pseudo Orde 2 where the R2 value is 0.9395 and 0.7274. Percent efficiency value of sugarcane activated carbon adsorption of Ca2+ dan Mg2+ ions on District Jati, Kudus well water is 14.44% and 8.94% and 40 minutes stirring time.

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