2023
DOI: 10.1007/s10311-023-01589-z
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Carbon dioxide separation and capture by adsorption: a review

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Cited by 49 publications
(25 citation statements)
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“…Accordingly, if one correlates these values to the fast kinetics, shaped form, and excellent thermal stability of MIL-160(Al), this shows the potential of this adsorbent for the development of cyclic adsorption processes concerning CCS (e.g., postcombustion) or BU. 62 The working capacity for a TSA process at 1.2 bar calculated in the temperature range of 313−343 K is around 1.07 mol kg −1 , whereas in a temperature range of 313−373 K, the same pressure becomes 1.85 mol kg −1 . Furthermore, the calculated working capacity for a PSA process at 313 K and pressure range between 0.5 and 7 bar is around 2.38 mol kg −1 , whereas at 343 K, it is a little bit smaller at 2.15 mol kg −1 , which can be compared with ones already reported at 298 K at the same pressure range: Mg-MOF-74: 2.1 mol kg −1 , zeolite 13X: 1.75 mol kg −1 , and UTSA-16: 1.44 mol kg −1 .…”
Section: Selectivity and Working Capacitymentioning
confidence: 98%
“…Accordingly, if one correlates these values to the fast kinetics, shaped form, and excellent thermal stability of MIL-160(Al), this shows the potential of this adsorbent for the development of cyclic adsorption processes concerning CCS (e.g., postcombustion) or BU. 62 The working capacity for a TSA process at 1.2 bar calculated in the temperature range of 313−343 K is around 1.07 mol kg −1 , whereas in a temperature range of 313−373 K, the same pressure becomes 1.85 mol kg −1 . Furthermore, the calculated working capacity for a PSA process at 313 K and pressure range between 0.5 and 7 bar is around 2.38 mol kg −1 , whereas at 343 K, it is a little bit smaller at 2.15 mol kg −1 , which can be compared with ones already reported at 298 K at the same pressure range: Mg-MOF-74: 2.1 mol kg −1 , zeolite 13X: 1.75 mol kg −1 , and UTSA-16: 1.44 mol kg −1 .…”
Section: Selectivity and Working Capacitymentioning
confidence: 98%
“…Carbon capture is a priority for CCUS; CO 2 mitigation methods are commonly grouped into three main categories: postcombustion, precombustion, and oxy-fuel combustion . During the postcombustion phase, CO 2 separation/capture technologies include membrane separation (e.g., polymeric membranes, inorganic membranes, mixed matrix membranes), physical adsorption (e.g., carbons, zeolites, MOFs, COFs), chemical adsorption and absorption (e.g., amines, ionic liquids, blends), and biological carbon fixation (e.g., Clostridia , algae, carbonic anhydrase). Wherein, the most feasible option is to utilize an alkaline aqueous solution to eliminate CO 2 from flue gas. However, these fluids have significant limitations, including low thermostability, strong corrosive behavior, high vapor pressure, toxicity, and volatility .…”
Section: Introductionmentioning
confidence: 99%
“…6−9 Understanding the PEI sorption mechanisms and the nature of the binding interactions with CO 2 under the variable humidity conditions encountered in practice is critical for designing efficient CO 2 capture systems. 10 However, probing these interactions at the molecular level can be challenging and is particularly complicated by reactive phenomena arising from the presence of water vapor and the presence of an added structural silica support. 11−15 There is a long history of using noncontact radar and dielectric spectroscopic methods to estimate moisture content in complex systems as the water content of soils, 16−18 and building materials such as concrete, masonry, composites, wood, and the asphalt material of roads, 19−22 and in a wide range of agricultural applications.…”
Section: ■ Introductionmentioning
confidence: 99%