Maximum adsorption oxygen (NMAX.OXIGENO) and nitrogen (NMAX.NITROGENO), Langmuir constants (KOXYGEN and KNITROGEN) and oxygen- nitrogen selectivity (αNITROG- OXIG) on modified natural mordenite MP [36].
Abstract
During the last years, the authors have synthesized, characterized, and studied the adsorption properties of nitroprussides, Prussian blue analogues, akaganeites, MeAPOs, metal–organic frameworks, and extremely high specific surface amorphous silica, which allowed the storage of about 11 wt.% of hydrogen in the form of ammonia. In this sense, using the solid-state reaction method, sol–gel methodologies, together with aluminosilicate, high silica and non-aluminosilicate zeolite synthesis methods, were described, moreover was explained how to prepare active carbons along with the synthesis of Prussian blue analogues (PBAs) and nitroprussides (NPs). In addition, the characterization of the materials of interest applying X-ray diffraction, thermogravimetric analysis, DRIFTS, and room-temperature Mossbauer spectrometry was discussed. Besides, the concepts that define physical adsorption and examples of adsorption data, which were tested with the help of the Dubinin, osmotic adsorption and Langmuir-type isotherms, were defined. Later, the methodology was described for the measurement of adsorption data with the help of the volumetric method. Moreover, a description of the thermodynamics of adsorption, along with the methodology for the calculation of calorimetric data with the help of heat flow calorimeters together with the measurement of differential heats of adsorption data was developed. Finally, the different interaction forces that make possible adsorption were discussed.
Keywords
- physical adsorption
- isotherms
- Dubinin and osmotic tests
- differential heats of adsorption
- nitroprussides
- Prussian blue analogues
- silica and natural zeolites
1. Introduction
The concept of “adsorption” was recommended by Kayser in 1881 to explain the growth in concentration of gas molecules on the adjacent surface of a solid adsorbent, an effect previously noted by Fontana and Scheele in 1777 [1]. In particular, majority of adsorbents useful for industrial applications have pores with hole dimensions in the nanometer region; in this pore-size zone, adsorption is on the one hand a significant methodology for the characterization of porous materials; to be exact, gas adsorption offers evidence concerning the mesopore area, volume and size of the pores together with the energetics of adsorption [2]. Also, gas adsorption is a vital unitary operation for sustainable energy and pollution abatement applications of nanoporous materials along with the industrial uses, where materials like metal organic framework molecular sieves, metal organic frameworks, Prussian blue analogues, mesoporous molecular sieves, pillared clays, silica, alumina, active carbons, titanium dioxides, magnesium oxides, carbon nanotubes together with zeolites and related materials are the most widely studied and applied adsorbents in Science and Technology [3].
In addition to their adsorption properties, nanoporous materials are a group of advanced materials with other excellent properties and applications in many fields, for example, waste water treatment [4, 5, 6], ionic conduction [7], ionic exchange [8], gas separation [9], membranes [10], catalysts [11], catalyst supports [12] and detergency [13].
The classification of the different pore widths of porous adsorbents was carried out by the International Union of Pure and Applied Chemistry (IUPAC); in this classification, adsorbent materials are categorized as those with pore diameters greater than 50 nm, named macroporous adsorbents, while mesoporous materials show pore diameters between 2 and 50 nm that are termed microporous; those adsorbents showing pore diameters between 0.3 and 2 nm, where, the pore width,
In addition, the clean surface of an adsorbent is characterized by the fact that the atoms that produce the surface have non-saturated bonds, fact producing an adsorption field above this surface; been the adsorption field the cause of the formation of a stockpile of molecules close to the adsorbent surface; this effect, i.e., adsorption, is a universal propensity of surface systems, given that throughout this process a reduction of the surface tension is experienced by the solid; been, adsorption the term applied to describe this process; whereas for the opposite, the term desorption is used [1].
Now it is necessary to state that the occupation of the adsorption space by adsorbed molecules in complex porous systems occurs roughly in the following form: initially, micropore filling takes place, with the adsorption process being controlled almost totally by the interaction of the adsorbed molecules with the pore walls; thereafter, at higher pressures, the external surface is covered, which is a monolayer and a multilayer adsorption on the walls of mesopores, and open macropores take place. Finally, capillary condensation occurs in the mesopores [2]. On the other hand, dynamic adsorption is a mass transfer between a mobile, solid, or liquid phase, and the adsorption bed packed in a reactor, been necessary to carry out the dynamic adsorption, a reactor, where the adsorption process will occur in the reactor adsorbent packed bed, been, the adsorbents normally used for these applications are active carbons, zeolites and related materials, silica, mesoporous molecular sieves, alumina, titanium dioxide, magnesium oxide, clays, and pillared clays [3].
2. Synthesis
2.1 Solid-state reaction method
Inorganic compounds are mixed, following stoichiometric proportions; after that, the powders are thoroughly milled and then finally thermally treated to get the required product, been, perovskites synthesized using this method [15, 16].
2.2 Sol-gel methodologies
These processes can be based on the hydrolysis condensation of metal alkoxides. In the important case of amorphous silica synthesis, silicic acid is first produced by the hydrolysis of a silicon alkoxide, formally a silicic acid ether; then, the global reaction continues as a condensation polymerization to form high molecular weight polysilicates, which connect together to produce a gel [17].
2.3 Aluminosilicate zeolites
These materials are normally synthesized in hydrothermal conditions using solutions that are composed of sodium hydroxide, sodium silicate and sodium aluminate, where three steps are observed during the synthesis process, i.e., induction, nucleation, and crystallization, which determine the specific zeolite produced by the applied reactants, along with the parameters used, such as temperature, pH, and time [18, 19].
2.4 High silica and non-aluminosilicate zeolites
In this case, the aluminosilicate synthesis is complemented with the addition of structure-directing agents (SDA), such as quaternary ammonium cations, linear or cyclic ethers, and coordination compounds. been, the first high-silica zeolites, that is, ETA, EU, NU, and the ZSM series, patented in the late 1960s, or early 1980s [20]; moreover, high silica zeolite can be as well synthesized using ethanol and seeds of the desired phase [21]; meanwhile, Microporous aluminophosphate molecular sieves, that is, non-aluminosilicate zeolites; such as: SAPO molecular sieves were obtained by incorporation of Si in the AlPO framework, while MeAPO molecular sieves are obtained by the inclusion of Ga, Be, Va, Co, Fe, Mg, Mn, Zn in the AlPO framework obtaining between others: gallophosphates, zincophosphates, beryllophosphates, vanadophosphates and ferrophosphates [22].
Active Carbon prepared with wood, lignite, peat, coconut, eucalyptus lignin, and apricot, cherry and olive stones under physical (a) and chemical activation (b) methods; i.e. [23, 24, 25]:
carbonization at 800–1000°C under inert gas, and activation under oxidizing agents, as a rule, carbon dioxide or water vapor.
chemical activation requires a treatment with: sulfuric acid, phosphoric acid, zinc chloride, potassium hydroxide at 400–1000°C, followed by the elimination of the dehydrating agent by meticulous washing.
Prussian blue analogues (PBAs) [26, 27] and nitroprussides (NPs) [28] are produced by mixing solutions of K3[Fe(CN)6], for the synthesis of Prussian blue analogues, and Na2[Fe(CN)5NO] for the synthesis of nitroprussides with a nitrate of the corresponding metal to get the corresponding PBAs and NPs.
3. Characterization
The X-ray Diffraction (XRD) methodology was used to determine the crystalline phases present in the natural and synthesized materials, together with the investigation of the nucleation and growth process during the synthesis of different materials to be used as adsorbents, ion exchangers and catalysts [29]. The XRD tests were carried out, at room temperature using a stage similar to an Anton Paar HTK-1200 N with an equipment similar to a Bruker D8 Advance system in a Bragg-Brentano vertical goniometer configuration, the angular measurements being made applying steps of 0.01° from 5 to 80°, using a Cu anode tube together with a Ni filter placed, prior to the detector, to eliminate Cu Kα radiation the one-dimensional detector was employed [26].
3.1 Thermo-gravimetric analysis (TGA)
The analytical test was carried out with an equipment similar to a TA, Q-500 instrument; the samples were placed onto a ceramic sample holder suspended from an analytical balance, suspended from an analytical balance; then the temperature was linearly scanned, from 25 to 300 C, at a heating rate of 5 C/min under a pure N2 flow of 100 mL/min. TGA testing process was carried out with a TA, Q-500 instrument, and the samples were placed onto a ceramic sample holder [27].
DRIFTS were gathered using equipment similar to a Thermo Scientific Nicolet iS10 FTIR spectrometer. The data of the hydrated and dehydrated samples were collected at a resolution of 4 cm−1 employing 100 scans per sample; a background, with pure KBr, was in all cases collected before the collection of the spectra. Both the hydrated and dehydrated samples were gathered at room temperature while flowing N2 (Praxair, 99.99%) at a rate of 50 cc/min; while, the dehydration of the studied samples was performed at 100°C for 2 h in N2 flow of 50 mL/min while the sample under test was included in the finger-sample-holder of the IR high temperature cell [28].
Room-temperature Mossbauer Spectrometry measurements were made with a system similar to a SEECo supplied spectrometer operating at constant acceleration mode with a 50 mCi 57Co γ-ray source in a Rh matrix made by Rietverc GmbH. The 1024-point raw data were folded and analyzed using WMOSS, a public domain Mossbauer spectral analysis program; the calibration was made with reference to α-Fe metal [30].
4. Definition and terms
4.1 Adsorption isotherm
It is the most important measurement made to characterize an adsorbent; it is defined as the relationship between the amount adsorbed,

Figure 1.
Graphic representation of the adsorption isotherm.
4.2 Physical and chemical adsorption
The gas adsorption process is normally considered a physical process, named physical adsorption, since the molecular forces involved in this process are usually of the van der Waals type. Meanwhile Chemical adsorption of gases in solid surfaces takes place in the case where during the adsorption process a reaction with exchange of electrons between the solid surface and the gas molecules with the formation of chemical bonds takes place, been, the adsorbent the solid phase and the adsorbate the gas phase [14].
4.3 Mobile and immobile adsorptions
Gas and vapor adsorption in solid adsorbents can be also classified as mobile adsorption, where the first case occurs when the adsorbed molecule is performed as a gas molecule is free to move within the adsorption space, or the instance of immobile adsorption, taking place in the case where the adsorbed molecule vibrates around an adsorption site [2, 3].
4.4 Monolayers and multilayers
For open surfaces, adsorption consists of a layer-by-layer loading process, where the first layer is filled as in the case when
4.5 Porous adsorbents
They are characterized by their specific surface area, denoted by S, and measured in (m2/g), in which the surface area is the outer surface, concretely, the area external to the micropores. If the adsorbents do not have micropores, the surface area and the outer surface area match; furthermore, the micropore volume is represented by WMP, measured in (cm3/g), whereas the total pore volume labeled W is the sum of the micropores and mesopore volumes [32] of the adsorbent, also measured in (cm3/g). Lastly, we have the pore size distribution (PSD), i.e., a plot of
4.6 Magnitude of adsorption
The interfacial layer is the non-homogeneous section of an adsorption system, i.e., between two neighboring bulk phases ( Figure 2 ), where the properties typifying this region are radically dissimilar from, but associated to, the properties of the bulk phases; in which, to deal with this system is assumed that in the ideal reference system, the concentration must be constant up to the Gibbs dividing surface (GDS) (see Figure 2 ); been, in an actual system [32]

Figure 2.
Gibbs dividing surface.
Then the total amount of gas molecules in the system measured in (mol/g) is
where
Finally the isotherm is calculated as follows:
where
Been, n and T, kept constants, then [29]:
where
Thereafter, using Eq. (4), based in the scheme of the volumetric adsorption equipment shown in Figure 11 , we get:
In Figure 11 , a schematic representation of volumetric gas adsorption measurement equipment is shown, where using the scheme, it is possible to show that:
Initially
where Pat is the atmospheric pressure and P1 is the measurement of pressure after expansion.
Substituting Eq. (
In this sense, using the proportions rule, we get:
Consequently applying the ideal gas law:
where
Number of moles in the dose volume and the volume provided by the displacement of the manometer.
5. Experimental determination of
V
a
and
V
a
′
and the numbers of mole gas adsorbed
n
aj
When the valve of the sample holder is opened, the gas is expanded; hence:
where:
This allows the calculation of Va, the so-called dead volume. Nevertheless the really expanded volume should consider the volume occupied by the adsorbent sample, i.e.:
And
According ideal gas low:
where:
which is the amount adsorbed in the tested sample, which plotted against the equilibrium pressure
6. The Dubinin adsorption isotherm equation
The Dubinin adsorption isotherm equation can be inferred by the application of the Dubinin’s Theory of Volume Filling, i.e., (where volume filling is a process which takes place by the filling of the adsorption space rather than the surface coverage), together with, the Polanyi’s adsorption potential [32]. In this regard, in 1914, Polanyi created perhaps the first convincing physical adsorption model. Mijail. M. Dubinin, a former pupil of Polanyi applied this model that essentially entailed a link between the adsorption space volume,

Figure 3.
Polanyi adsorption model.
In which,
where
Now, applying the Weibull distribution function, the relation between the amount adsorbed,
where
It is possible, as well, to express the Dubinin adsorption isotherm equation in linear form:
which is a very powerful tool for the description of the experimental data of adsorption in microporous material.
In Figure 4 is shown the Dubinin plot of N2 adsorption data at 77 K in the pressure range: 0.001 < P/Po < 0.03, in a high silica commercial H-Y zeolite, precisely, the acid Y zeolite labeled CBV-720, manufactured by PQ corporation; where, adsorption data was gathered in an Autosorb-1 automatic volumetric gas adsorption system [26]; been evidently the experimental data correctly fitted by Eq. (12)

Figure 4.
Dubinin plot sample CBV-720 N2 at 77 K [
Recapitulating, the concrete form to made the linear Dubinin plot as represented in Figure 4 was as follows:
where
Nevertheless, this fitting process can be as well made using a non-linear regression method; in which, the fitting process is carried out with a program based on a least square procedure, allowing the calculation of the best fitting parameters of the Eq. (12), that is,
As another example, in Figure 4 , the use of the Dubinin equation in the measurement of the micropore volume, of a nickel nitroprusside (Ni-NP), is reported [34]( Figure 5 ).

Figure 5.
Dubinin plot of carbon dioxide adsorption on nickel nitroprusside [
7. Osmotic and Langmuir-type adsorption isotherms
Within the frame of the osmotic theory of adsorption, the adsorption phenomenon in a microporous adsorbent, for example a zeolite, is considered as the “osmotic” equilibrium between two solutions, i.e., vacancy plus molecules of different concentrations and the molecules in the gas phase. The solutions are formed in the micropores, and the gas phase, where the solvents are the vacancies, i.e., the vacuum [33] been, these solutions in equilibrium, in the case when one of the solutions is submerged in an external field.
Where the main supposition, made within the frame of this adsorption theory is that the role of the adsorption field could be simulated by;
Consequently, if we multiply the previous equation by
where
It is termed the osmotic isotherm of adsorption, or the Sips, or Bradleys isotherm equation, where this isotherm equation, fairly well, describes the experimental data of adsorption in zeolites, and other micoroporous materials; the linear form of the osmotic equation being expressed as follows:
where
In
Figure 6
, the linear plot of Eq. (14) is shown, using B = 0.5, fitting NH3 at 300 K adsorption results in Mg-CMT, i.e., homoionic magnesium natural zeolite, concretely a blend of mordenite (39 wt. %), clinoptilolite (42 wt. %) along with additional phases (15 wt. %), where these supplementary phases are: montmorillonite (2–10 wt. %), calcite (1–6 wt. %), feldspars (0–1 wt. %), volcanic glass together with quartz (1–5 wt. %). These results were measured in a Pyrex glass volumetric adsorption vacuum system, consisting of sample holder, dead volume, dose volume, U-tube manometer, and thermostat [32]; this plot allowed us to calculate the maximum adsorption capacity of this zeolite, which is

Figure 6.
Linear osmotic plot, with B = 0.5 of the adsorption data of NH3 at 300 K in magnesium homoionic CMT zeolite [
The fitting process of the osmotic isotherm equation could be also carried out with the help of a non-linear regression method, where the fitting process allows us to calculate the best fitting parameters of the Eq. (13), i.e.,
Further adsorption isotherms are reported below [35] ( Figures 7 and 8 ):

Figure 7.
Nitrogen adsorption on zeolite 5 a (Ca, Na-LTA) at 291 K.

Figure 8.
Ethane adsorption on zeolite 13 X (Na-FAU) at 291 K.
Additionally, the adsorption of oxygen (O2) and nitrogen (N2) in modified natural mordenite from the Palmarito, Santiago de Cuba, Cuba, deposit, composed of mordenite (80 wt.%), clinoptilolite (5 wt.%), and other phases (15 wt.%), where the other phases included montmorillonite (2–10 wt.%), quartz (1–5 wt.%), calcite (1–6 wt.%), feldspars (0–1 wt.%), and volcanic glass [2]. Labeled MP are reported in Table 1 , where H means acid; NH, ammonia; Li, Lithium; Na, Sodium; K, Potassium; Mg, Magnesium; Ca, Calcium; Sr., Strontium; Ba, Barium zeolite; where, the oxygen nitrogen selectivity is given by [36].
ZEOLITES | NMAX.OXYGEN
(mmol/g) |
NMAX.NITROGEN
(mmol/g) |
KOXYGEN
(Torr)−1×10−3 |
KNITROGEN
(Torr)−11×10−3 |
αNITROG- OXIG |
---|---|---|---|---|---|
H-MP | 0.24 | 0.5 | 1.3 | 2.3 | 3.7 |
NH-MP | 0.10 | 0.25 | 0.12 | 2.0 | 42 |
Li-MP | 0.21 | 0.86 | 1.8 | 3.0 | 6.8 |
Na-MP | 0.29 | 0.63 | 9.3 | 2.0 | 4.7 |
K-MP | 0.07 | 0.26 | 3.1 | 3.7 | 4.4 |
Mg-MP | 0.13 | 0.56 | 0.21 | 3.9 | 84 |
Ca-MP | 0.27 | 0.56 | 1.4 | 4.8 | 7.1 |
Sr-MP | 0.32 | 0.59 | 1.2 | 4.6 | 7.1 |
Ba-MP | 0.23 | 0.75 | 1.5 | 1.9 | 4.1 |
Table 1.
where
It is necessary now to state that the framework of mordenite shows an orthorhombic unit cell displaying the space group Cmcm or Cmc21; in this sese, the unit cell of the Na cationic form has dimensions a = 18.13 Å, b = 20.49 Å, and c = 7.52 Å, along with the following composition: Na8Al8Si40 O96 · 24H2O; composed fundamentally of a channel system composed of a 5-membered ring system parallel to [001], having a free diameter of 6.6 Å, interconnected by smaller channels, parallel to [010], of 2.8 Å free diameter. However, the existence of stacking faults in the framework reduces the effective diameter of the channels to about 4 Å [37]. Moreover, the volume of the unit cell is 2794
The application of the grand canonical ensemble (GCE) allows us to handle the adsorption process in microporous materials such as zeolites and related materials. In this case, the whole zeolite is considered a GCE, i.e., the zeolite cavities or channels are considered in the frame of this model as independent open systems constituting the ensemble, additionally the adsorption field within the cavities is energetically homogeneous, i.e., the adsorption field is the same at any site within the adsorption space; besides, each cage can accommodate
where
Is the channel or cavity grand canonical partition function; been,
Now it is necessary to state that within the frame of the adsorption process in zeolites and related materials two cases are possible; that is, inmobile (I) or mobile (M) adsorption, been in the first and second cases, the canonical partition functions for the inmobile (
Now since:
Consequently:
With:
Equation (19) is of the Fowler-Guggenheim type (FGT), but describing volume filling rather than surface covering, where both equations reduce to Langmuir-type (LT) isotherm equations, as well describing volume filling. Moreover, the osmotic isotherm equation and the FGT types have the same mathematical form in the case where B = 1 in the osmotic equation, as well as are equivalent to the Langmuir T type equations, when
To test these isotherm types, the FGT and LT type equations can be written as follows [2]:
While the linear form of the LT type isotherms is

Figure 9.
Carbon dioxide adsorption on Ni-NP at 273 and 300 K [
8. t-plot method
The t-plot method suppose that the adsorbed phase as a liquid adhered film over the solid surface, the model was proposed by Halsey, De Boer, and coworkers following ideas previously proposed by Frenkel-Halsey-&-Hill which stated that it is possible to calculate,
Attraction by the adsorption field is given by
Subsequently, since the adsorption process considered in the present model is a multilayer one, then
where
Thereafter, supposing again, that the surface liquid film is assumed of uniform width,
where
The following relation
which is the Halsey equation, valid for N2 at 77 K or the equation used by De Boer. Moreover, the following expression:
is as well used for the application of the t-plot methodology. Now it is necessary to state that the molar volume of liquid nitrogen at 77 K is
The method to calculate,

Figure 10.
t-plot for the adsorption of
The linear regression is made, then the intercept,
9. Thermodynamics of adsorption
Adsorption is a general tendency of matter, and during its occurrence, a decrease in the surface tension is experienced by the solid. For this reason, adsorption is a spontaneous process, where the Gibbs free energy decreases, i.e., ΔG < 0. Besides, in the course of physical adsorption, molecules from a chaotic bulk phase are transferred to a relatively ordered adsorbed state, since in the adsorbed state molecules can only move within the surface or a pore; consequently, in the course of adsorption by the entire system, a reduction of entropy takes place, i.e., ΔS < 0; subsequently [2, 32]:
Consequently, the adsorption process releases heat, i.e., it is an exothermic process. Consequently, it is stimulated by a reduction of the adsorption experiment temperature.
As a matter of fact, the main thermodynamic relation for a bulk mixture system is given by:
where S is their entropy, U is the internal energy, V is the volume, T is the temperature, μi is the chemical potential, and ni is the constituent number of moles included in the system [18]. Now it is supposed that the adsorbent together with the adsorbed gas is a solid solution, labeled, system aA; thereafter, using the proposed scheme, it is possible to deduce the following equation, which thermodynamically describes the aA system [2, 32]:
where UaA, SaA, and VaA are the internal energy, entropy, and volume of the system aA, respectively, and μa and μA are the chemical potentials of the adsorbate, a, and the adsorbent, A, while na and nA are the number of moles of the adsorbate and the adsorbent in the system aA, respectively. Now if we define
As a result:
where
where qiso is the enthalpy of desorption, or the isosteric heat of adsorption, which is calculated with the help of adsorption isotherms. An additional significant adsorption heat is the differential heat of adsorption, since when an adsorbate contacts an adsorbent, heat is released. In our case, the thermal effect produced was measured with the help of a thermocouple placed inside the adsorbent and referred at room temperature ( Figure 11 ), a variety of the Tian–Calvet heat-flow calorimeter [32]. This calorimetric methodology is characterized by the fact that the difference of temperature among the tested adsorbent and a thermostat is determined; therefore, in this heat-flow calorimeter, the produced thermal energy in the adsorption cell is permitted to flow with no limitations to the thermostat. In the calorimeter constructed by us, heat flows throughout a thermocouple; thereafter, the voltage produced by the thermocouple, which is proportional to the thermal power, is amplified and recorded in an x-y plotter (see Figure 11 ); in which, the actual thermal effect generated is the integral heat of adsorption, measured using the Eq. (2)

Figure 11.
Adsorption volumetric equipment.
where
The heat-flow calorimeter used consisted of the high vacuum line for adsorption measurements applying the volumetric method; as reported in Figure 11 , the equipment comprises the following: a Pyrex glass, vacuum system including a sample holder, a dead volume, a dose volume, a U-tube manometer, and a thermostat, including now a thermocouple immersed in the adsorbent bed, which was coupled to an x-y plotter.
In Figure 12 , the measurement of the differential heat of adsorption for the adsorption of carbon dioxide in the natural mordenite labeled MP is reported, which is a mordenite from the Palmarito, Santiago de Cuba, Cuba, deposit (mordenite (80 wt.%), clinoptilolite (5 wt.%), together with montmorillonite (2–10 wt.%), quartz (1–5 wt.%), calcite (1–6 wt.%), feldspars (0–1 wt.%), and volcanic glass) [2]. In Figure 12 , the obtained data are shown indicating that CO2 adsorption process in this zeolite is energetically heterogeneous; i.e., the heat of adsorption is a diminishing function of the zeolite micropore volume recovery, i.e., θ = na/nmax. That is, the plot of qdiff versus θ shows the following: two steps, one at 90 kJ/mol and the other at 70 kJ/mol, where was released, moderately high values of the adsorption heats, indicating that CO2 molecules powerfully interact through their quadrupole moments with the mordenite framework; after that, a reduction of the adsorption heat is found, up to a value corresponding to the bulk heat of condensation of the CO2 molecules [26, 27, 28].

Figure 12.
Plot of qdiff vs. θ for the adsorption of CO2 at 300 K in the MP zeolite [
10. Adsorption interaction fields
If a molecule contacts a solid adsorbent, it is exposed to various interaction fields, such as dispersion attraction, φD; repulsion, φR; induced polarization, φP; permanent dipole, φEμ; quadrupole, φEQ; and sorbate-sorbate, φAA.
Specific interactions as the acid-base interaction with the active site, φAB, if the surface contains hydroxyl bridge groups.
The dispersion or London forces among adsorbed nonpolar molecules and all types of adsorbents takes place when the transient dipoles turn out to be correlated; then, the dipoles of the nonpolar adsorbed species prompt a dipole in the atoms of the adsorbed species that act together to reduce the energy of the adsorption system. Hence, due to the correlation, the prompted dipoles created in the entire arrangement do not disappear, generating a dipole–dipole collaboration, dispersion interaction being intensity dependent on the polarizability of the adsorbate molecule and the adsorbent surface atom [40].
Additionally, the electrostatic contribution to the potential includes the dipole induced, dipole permanent and quadrupole terms, where, the induced polarization term occurs when nonpolar molecules within an electric field are polarized, and then an induced dipole moment is produced, the permanent dipole and quadrupole terms being caused by molecules whose structures produce permanent dipoles and quadrupoles; for example, H2O, H2S, SO2, and NH3 are molecules with a high dipole moment, whereas CO2 is a molecule with a high quadrupole moment [1].
The electrostatic attractive interactions are stronger than the dispersion interactions; however, dispersion is the fundamental attractive force present during adsorption in all adsorbate-adsorbent systems, for example, in the case of molecules like H2, Ar, CH4, N2, and O2. Given that the dipole moments of these molecules are zero, the quadrupole moment is very low or absent, and the polarization effect will only be noticeable in the case of adsorbents with high electric fields; the dispersion and repulsion interactions are responsible for the adsorption effect present in all adsorption gas-solid systems; therefore, they are nonspecific interactions [2].
References
- 1.
Breck DW. Zeolite Molecular Sieves. New York: John Wiley & Sons; 1974. pp. 635-700 - 2.
Roque-Malherbe R. Physical Chemistry of Materials. Energy and Environmental Applications. Boca Raton Florida: CRC Press; 2009. pp. 275-338 - 3.
Roque-Malherbe R. Adsorption and Diffusion in Nanoporous Materials. Boca Raton, FL, USA: CRC Press; 2018. pp. 153-287 - 4.
Benitez F, Travieso L, Sanchez E, Roque-Malherbe R. Waste water treatment technology. In: International Conference on Advanced Waste Water Treatment and Reclamation; September 1989; Cracow, Poland - 5.
Misaelides P. Application of natural zeolites in environmental remediation. Microporous and Mesoporous Materials. 2011; 144 :15-18 - 6.
Wang S, Peng Y. Chemical Engineering Journal. 2010; 156 :11-24 - 7.
McKeen JC. Proton and ion conduction in microporous materials [Ph. D. Thesis]. Pasadena, CA, USA: California Institute of Technology; 2009 - 8.
Zagorodni AA. Ion Exchange Materials: Properties and Applications. Amsterdam, the Netherlands: Elsevier Science & Technology Books; 2006 - 9.
Lu C. Nanoporous materials chemistry. From gas separation to high pressure chemistry [Ph. D. Thesis]. Bethlehem, PA, USA: Lehigh University; 2017 - 10.
Caro J, Noack M. Zeolite membranes?recent developments and progress. Microporus and Mesoporous Materials. 2008; 115 :215-233 - 11.
Thomas JM, Thomas WJ. Principle and Practice of Heterogeneous Catalysis. New York: VCH Publishers; 1997 - 12.
Schlögl R. In: Ertl G, Knozinger H, Weitkamp J, editors. Preparation of Solid Catalysts. Weinheim, Germany: WileyVCH; 1999. pp. 11-28 - 13.
Thomas TL. Process for cation separation using zeolite materials. U. S. Patent 3,033,641; 1962 - 14.
McNaught AD, Wilkinson A. IUPAC Compendium of Chemical Technology. Oxford: Blackwell Scientific Publications; 1997 - 15.
Do JL, Friscic T. ACS Central Science. 2017; 3 :13-19 - 16.
Sanchez DA, Ortega N, Kumar A, Roque-Malherbe R, Polanco R, Katiyar RS, et al. Symmetries and multiferroic properties of novel room-temperature magnetoelectrics: Lead iron tantalate?Lead zirconate titanate (PFT/PZT). AIP Advances 2011; 1 :042169-1-042169-14 - 17.
Brinker C, Scherrer G. Introduction. In: Brinker C, Scherrer G, editors. Sol-Gel Science. 1st ed. The Physics and Chemistry of Sol-Gel Processing. New York: Academic Press; 2013. pp. 1-18 - 18.
Robson H, editor. Verified Synthesis of Zeolitic Materials. Amsterdam, the Netherlands: Elsevier; 2001 - 19.
de las Pozas C, Diaz Quintanilla D, Perez Pariente J, Roque Malherbe R, Magi M. Hydrothermal transformation of natural clinoptilolite to zeolites Y and P1: Influence of the Na, K content. Zeolites Zeolites. 1989; 9 :33-39 - 20.
Martens JA, Jacobs PA. Synthesis of High Silica Aluminosilicate Zeolites. Vol. 33. Amsterdam: Elsevier; 1987 - 21.
Gonzales E, Lariot C, Villegas R, Morales F, Cañizares H, Herrero E, et al. Influence of temperatura and syntheisis time in the acidity and morphology of ZSM-5 zeolites. Revista CENIC. 2001; 32 :43-50 - 22.
Roque-Malherbe R, Lopez-Cordero R, Gonzales-Morales JA, Oñate-Martinez J, Carreras-Gracial M. A comparative study of MeAPO molecular sieves with AFI structure type. Zeolites. 1993; 13 :481-484 - 23.
Marsh H, Rodriguez Reynoso F. Active Carbon. Amsterdam: Elsevier; 2006 - 24.
Bansal RC, Gayal M. Activated Carbon Adsorption. Boca Raton, FL, USA: CRC Press-Taylor and Francis; 2005 - 25.
Roque-Malherbe R. Physical Chemistry of Materials. Energy and Environmental Applications. Boca Raton Florida: CRC Press; 2009. pp. 103-135 - 26.
Roque-Malherbe R, Lugo F, Polanco R. Applied Surface Science. 2016; 385 :360-367 - 27.
Roque-Malherbe R, Carballo E, Polanco R, Lugo F, Lozano C. Structure and adsorption properties of a porous cooper hexacyanoferrate polymorph. Journal of Physics and Chemistry of Solids. 2015; 86 :65-73 - 28.
Roque-Malherbe R, Uwakweh ONC, Lozano C, Polanco R, Hernandez-Maldonado A, Fierro P, et al. Structural effects and interactions of carbon dioxide molecules adsorbed on Ni, Zn, and Cd nitroprussides. Journal of Physical Chemistry C. 2011; 115 :15555-15569 - 29.
Roque-Malherbe R. Physical Chemistry of Materials. Energy and Environmental Applications. Boca Raton Florida: CRC Press; 2009. pp. 137-218 - 30.
Reguera E, delas Pozas C, Diaz Aguila C, Roque Malherbe R. Mössbauer study of hydrothermal transformation of natural clinoptilolite into Y and P1 zeolites. Journal of Solid State Chemistry. 1991; 94 :215-219 - 31.
Everett DH, Ottewill RH. Surface Area Determination, International Union of Pure and Applied Chemistry. London: Butterworth; 2103 - 32.
Roque-Malherbe R. Adsorption and Diffusion in Nanoporous Materials. Boca Raton, FL, USA: CRC Press; 2018. pp. 35-71 - 33.
Bering BP, Dubinin MM, Serpinskii VV. On thermodynamics of adsorption in micropores. Journal of Colloid and Interface Science. 1972; 38 :185-194 - 34.
Roque-Malherbe R, Lozano C, Polanco R, Marquez F, Lugo F, Hernandez-Maldonado A, et al. Study of carbon dioxide adsorption on a Cu-nitroprusside polymorph. Journal of Solid State Chemistry. 2011; 184 (5):1236-1244 - 35.
Venero A, C and L Science and Technology, Hiahleah, FL, USA, Personal Communications - 36.
Autie M, de las Pozas C, Balmaceda J. Revista CENIC. Ciencias Químicas. 2003; 34 :41-44 - 37.
Lide RD, editor. CRC Handbook of Chemistry and Physics. 88th ed. Boca Raton, Florida: Taylor & Francis Group; 2008 - 38.
Voogd J, Scholten JJF, Van Bekkum H. Nitrogen adsorption isotherms at 77 K have been measured of H-ZSM-5 samples. Colloids and Surfaces. 1991; 55 :163-171 - 39.
Marquez-Linares F, Roque-Malherbe R. Journal of Nanoscience and Nanotechnology. 2006; 6 :1-5 - 40.
Roque-Malherbe R. Adsorption and Diffusion in Nanoporous Materials. Boca Raton, FL, USA: CRC Press; 2018. pp. 35-48