Experimental and model investigations of CO2 adsorption onto fly ash zeolite surface in dynamic conditions

2020 ◽  
Vol 15 ◽  
pp. 100222 ◽  
Author(s):  
Denitza Zgureva ◽  
Silviya Boycheva
2019 ◽  
Vol 19 (3) ◽  
pp. 475-483 ◽  
Author(s):  
Muvumbu Jean-Luc Mukaba ◽  
Alechine Emmanuel Ameh ◽  
Chuks Paul Eze ◽  
Leslie Felicia Petrik

2019 ◽  
Vol 96 ◽  
pp. 374-381 ◽  
Author(s):  
Yafei Guo ◽  
Chang Tan ◽  
Peng Wang ◽  
Jian Sun ◽  
Junjie Yan ◽  
...  

2019 ◽  
Vol 191 (9) ◽  
pp. 1484-1498 ◽  
Author(s):  
V. Gargiulo ◽  
M. Alfè ◽  
F. Raganati ◽  
A. Zhumagaliyeva ◽  
Y. Doszhanov ◽  
...  

Materials ◽  
2018 ◽  
Vol 11 (12) ◽  
pp. 2424 ◽  
Author(s):  
Bao-guo Fan ◽  
Li Jia ◽  
Yan-lin Wang ◽  
Rui Zhao ◽  
Xue-song Mei ◽  
...  

In order to obtain the adsorption mechanism and failure characteristics of CO2 adsorption by potassium-based adsorbents with different supports, five types of supports (circulating fluidized bed boiler fly ash, pulverized coal boiler fly ash, activated carbon, molecular sieve, and alumina) and three kinds of adsorbents under the modified conditions of K2CO3 theoretical loading (10%, 30%, and 50%) were studied. The effect of the reaction temperature (50 °C, 60 °C, 70 °C, 80 °C, and 90 °C) and CO2 concentration (5%, 7.5%, 10%, 12.5%, and 15%) on the adsorption of CO2 by the adsorbent after loading and the effect of flue gas composition on the failure characteristics of adsorbents were obtained. At the same time, the microscopic characteristics of the adsorbents before and after loading and the reaction were studied by using a specific surface area and porosity analyzer as well as a scanning electron microscope and X-ray diffractometer. Combining its reaction and adsorption kinetics process, the mechanism of influence was explored. The results show that the optimal theoretical loading of the five adsorbents is 30% and the reaction temperature of 70 °C and the concentration of 12.5% CO2 are the best reaction conditions. The actual loading and CO2 adsorption performance of the K2CO3/AC adsorbent are the best while the K2CO3/Al2O3 adsorbent is the worst. During the carbonation reaction of the adsorbent, the cumulative pore volume plays a more important role in the adsorption process than the specific surface area. As the reaction temperature increases, the internal diffusion resistance increases remarkably. K2CO3/AC has the lowest activation energy and the carbonation reaction is the easiest to carry out. SO2 and HCl react with K2CO3 to produce new substances, which leads to the gradual failure of the adsorbents and K2CO3/AC has the best cycle failure performance.


Fuel ◽  
2020 ◽  
Vol 276 ◽  
pp. 118041 ◽  
Author(s):  
Gabriele Verrecchia ◽  
Lorenzo Cafiero ◽  
Benedetta de Caprariis ◽  
Alessandro Dell'Era ◽  
Ida Pettiti ◽  
...  
Keyword(s):  
Fly Ash ◽  

2020 ◽  
Vol 34 (9) ◽  
Author(s):  
Seth Sheeba Thavamani ◽  
Murugesan Sudharsan ◽  
Anitha Santhana Mariya ◽  
Devarajan Suresh ◽  
Arlin Jose Amali ◽  
...  

2014 ◽  
Vol 54 (7) ◽  
pp. 1839-1849 ◽  
Author(s):  
Joanna Kluczka ◽  
Jolanta Trojanowska ◽  
Maria Zołotajkin

2010 ◽  
Vol 5 (3) ◽  
pp. 302-308
Author(s):  
Herry Poernomo ◽  
Noor Anis Kundari ◽  
Burhani J W

An investigation of the contribution of fly ash in the fly ash-zeolite mixture as the backfill material on the shallow land burial of radioactive waste has been done. The experiment objective is to know the effect of zeolite particle size and fly ash-zeolite weight ratio on physical properties such as permeability (K) and dispersion characteristic such as effective dispersion coefficient (De) in the fly ash-zeolite form as backfill material. The experiment was carried out by the fixed bed method in the column filled by the fly ash-zeolite mixture with a fly ash-to-zeolite weight percent ratio of 100/0, 80/20, 60/40, 40/60, 20/80, 0/100 in the water saturated condition flown by uranyl nitrate solution at concentration (Co) of 500 ppm. The concentration of uranium in the effluents in interval 15 minutes represented as Ct was analyzed by spectrophotometer, then using Co and Ct, data effective dispersion coefficient (De) in the backfill material were determined. The experiment data showed that -400 mesh fly ash and -70+80 mesh zeolite on fly ash-to-zeolite with weight percent ratio of 40/60 with K = 5.00x10-5cm/second and De = 1.11.10-5 cm2/second can be used as backfill material. Keywords: backfill material, fly ash, radioactive waste, zeolite


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