Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols

The aim of the study is to determine the effects of structure and content of X, CX in the oxides X/SiO₂ (X = Al₂O₃, TiO₂, Al₂O₃/TiO₂) on the surface characteristics. The low-temperature nitrogen adsorption isotherms on the surface of 12 individual and mixed fumed oxides of Si, Ti and Al, as proxies...

Ausführliche Beschreibung

Gespeichert in:
Bibliographische Detailangaben
Datum:2019
Hauptverfasser: Bazylevska, M.S., Bogillo, V.I.
Format: Artikel
Sprache:English
Veröffentlicht: Національний антарктичний науковий центр МОН України 2019
Schriftenreihe:Український антарктичний журнал
Schlagworte:
Online Zugang:http://dspace.nbuv.gov.ua/handle/123456789/168292
Tags: Tag hinzufügen
Keine Tags, Fügen Sie den ersten Tag hinzu!
Назва журналу:Digital Library of Periodicals of National Academy of Sciences of Ukraine
Zitieren:Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols / M.S. Bazylevska, V.I. Bogillo // Український антарктичний журнал. — 2019. — № 1 (18). — С. 3-17. — Бібліогр.: 40 назв. — англ.

Institution

Digital Library of Periodicals of National Academy of Sciences of Ukraine
id irk-123456789-168292
record_format dspace
spelling irk-123456789-1682922020-04-30T01:26:29Z Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols Bazylevska, M.S. Bogillo, V.I. Геолого-геофізичні дослідження The aim of the study is to determine the effects of structure and content of X, CX in the oxides X/SiO₂ (X = Al₂O₃, TiO₂, Al₂O₃/TiO₂) on the surface characteristics. The low-temperature nitrogen adsorption isotherms on the surface of 12 individual and mixed fumed oxides of Si, Ti and Al, as proxies for the Antarctic atmospheric mineral aerosols, were measured by volumetric method. Метою роботи було визначення впливу природи та вмісту X, CX в оксидах X/SiO₂ (X = Al₂O₃, TiO₂, Al₂O₃/ TiO₂) на характеристики їх поверхні. Методом волюметрії виміряні низькотемпературні ізотерми адсорбції азоту на поверхні 12 індивідуальних і змішаних пірогених оксидів Si, Ti та Al, як компонентів мінеральних аерозолів в атмосфері Антарктики. 2019 Article Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols / M.S. Bazylevska, V.I. Bogillo // Український антарктичний журнал. — 2019. — № 1 (18). — С. 3-17. — Бібліогр.: 40 назв. — англ. 1727-7485 http://dspace.nbuv.gov.ua/handle/123456789/168292 504.3.054: 544.723.23: 544.772: 547-302 en Український антарктичний журнал Національний антарктичний науковий центр МОН України
institution Digital Library of Periodicals of National Academy of Sciences of Ukraine
collection DSpace DC
language English
topic Геолого-геофізичні дослідження
Геолого-геофізичні дослідження
spellingShingle Геолого-геофізичні дослідження
Геолого-геофізичні дослідження
Bazylevska, M.S.
Bogillo, V.I.
Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols
Український антарктичний журнал
description The aim of the study is to determine the effects of structure and content of X, CX in the oxides X/SiO₂ (X = Al₂O₃, TiO₂, Al₂O₃/TiO₂) on the surface characteristics. The low-temperature nitrogen adsorption isotherms on the surface of 12 individual and mixed fumed oxides of Si, Ti and Al, as proxies for the Antarctic atmospheric mineral aerosols, were measured by volumetric method.
format Article
author Bazylevska, M.S.
Bogillo, V.I.
author_facet Bazylevska, M.S.
Bogillo, V.I.
author_sort Bazylevska, M.S.
title Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols
title_short Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols
title_full Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols
title_fullStr Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols
title_full_unstemmed Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols
title_sort adsorption properties of the fumed individual and mixed si, ti and al oxides as proxies for the antarctic atmospheric mineral aerosols
publisher Національний антарктичний науковий центр МОН України
publishDate 2019
topic_facet Геолого-геофізичні дослідження
url http://dspace.nbuv.gov.ua/handle/123456789/168292
citation_txt Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides as proxies for the Antarctic atmospheric mineral aerosols / M.S. Bazylevska, V.I. Bogillo // Український антарктичний журнал. — 2019. — № 1 (18). — С. 3-17. — Бібліогр.: 40 назв. — англ.
series Український антарктичний журнал
work_keys_str_mv AT bazylevskams adsorptionpropertiesofthefumedindividualandmixedsitiandaloxidesasproxiesfortheantarcticatmosphericmineralaerosols
AT bogillovi adsorptionpropertiesofthefumedindividualandmixedsitiandaloxidesasproxiesfortheantarcticatmosphericmineralaerosols
first_indexed 2025-07-15T03:05:08Z
last_indexed 2025-07-15T03:05:08Z
_version_ 1837680515620012032
fulltext 3 Cite: Bazylevska M. S., BogilloV. I. Adsorption properties of the fu- med individual and mixed Si, Ti and Al oxides as proxies for the An- tarctic atmospheric mineral aerosols. Ukrainian Antarctic Journal, 2019. № 1(18), 3—17. UDC: 504.3.054: 544.723.23: 544.772: 547-302 M. S. Bazylevska*, V. I. Bogillo Institute of Geological Sciences, National Academy of Sciences of Ukraine, 55B O. Gonchara Str., Kyiv, 01054, Ukraine * Corresponding author: bazilevskaya1955@gmail.com ADSORPTION PROPERTIES OF THE FUMED INDIVIDUAL AND MIXED SI, TI AND AL OXIDES AS PROXIES FOR THE ANTARCTIC ATMOSPHERIC MINERAL AEROSOLS ABSTRACT. The aim of the study is to determine the effects of structure and content of X, C X in the oxides X/SiO 2 (X = Al 2 O 3 , TiO 2 , Al 2 O 3 /TiO 2 ) on the surface characteristics. The low-temperature nitrogen adsorption isotherms on the surface of 12 indi- vidual and mixed fumed oxides of Si, Ti and Al, as proxies for the Antarctic atmospheric mineral aerosols, were measured by volumetric method. The specific surface areas of the oxides, S BET were calculated by using the Brunauer–Emmett–Teller (BET) theory. The dependence between C X and S BET is not obeyed for the mixed oxides, which can be caused by effects of the reaction temperature of MCl n (M = Si, Ti and Al) hydrolysis in the oxygen/hydrogen flame and by different concentration ratios of O 2 , H 2 and MCl n on the structural characteristics of the primary particles and their aggregates. The N 2 adsorption energy distribu- tions of the oxides surface were calculated by the regularization procedure. It was demonstrated that the surfaces are character- ized by high energetic heterogeneity. Result. The Zero-Adsorption Isotherm (ZAI) approach was applied to describe the N 2 adsorption in the whole range of its pressures. The ZAI derived in approximation of adsorbed vapor as a set of molecular clusters. The specific surface areas for the oxides, A s , maximal numbers of the molecules in the adsorbed clusters, thicknesses of the ad- sorbed liquid film and the free surface energies of the oxides in the absence of adsorption, γS0, were calculated using the ZAI equations. The A s correlates well with SBET and it measures 77.5% of the S BET . The γS0 increases as the N 2 average adsorption energy grows. The dependence between γS0 and C X (taking into account γS0 for X) is not obeyed for the mixed oxides. The γS0 for SiO 2 , Al 2 O 3 and TiO 2 rises as the permittivity and the index of refraction increase. The γS0 is within the range of dispersive com- ponents of free surface energy, which is determined by other experimental methods and calculated using the Lifshitz’ theory. The obtained parameters allow estimate the activity of the oxide surface with respect to trace gases in the Antarctic atmosphere that is necessary for calculating their partition coefficients between particles and the atmosphere and the kinetics of their removal. Keywords: mineral aerosols, Antarctic atmosphere, fumed individual and mixed Si, Ti and Al oxides, nitrogen adsorption. Геолого-геофізичні дослідження Geological and Geophysical Research ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) INTRODUCTION Atmospheric aerosols play a major role in Earth’s cu rrent climate due to their impact on the global radiation balance (Seinfeld and Pandis, 2006). Aero- sols also lead to formation of cloud droplets and ice crystals by serving as cloud condensation nuclei (CCN) and ice nuclei particles (INP). Aerosols affect the life time of clouds, size distributions of cloud droplets, glaciation rates and the distribution of water mass in different atmospheric layers. Unfortunately, aerosols are still the least understood and constrained aspects of the climate system. The uncertainty of aerosols’ climate impacts arise from the fact that how an aerosol affects the radiative balance is a function of both an aerosol’s chemical composition and phy- si cal properties (e.g. size, shape). Both chemical and physical properties of aerosols are functions of emi- ssion sources, atmospheric processing pathways, and lifetime in the atmosphere. 4 ISSN 1727-7485. Ukrainian Antarctic Journal. 2019, № 1 (18) M. S. Bazylevska, V. I. Bogillo The atmosphere above Antarctica constitutes the cleanest part of the Earth's troposphere which allows here to study the composition and temporal change of the background atmosphere without any direct impact of civilization. Furthermore, with the exception of very few rocky terrains, the Antarctic continent is largely free of aerosol sources, so that the main part of the particles must be advected by long-range transport to Antarctica or has its source region in the surroun- ding Southern Ocean. Due to this unique position, Antarctica is an outstanding place to document long- term changes of the composition of our atmosphere in the industrial period. The Antarctic climate system can be linked with aerosol particles by complex feed- back processes that involve aerosol-cloud inter actions. In addition, because there are less anthropogenic emission sources in Antarctica, it is a suitable place to study the formation and growth processes of the natural aerosol particles. Mineral dust is extremely important in the nucleation processes, as sites for heterogeneous chemistry. Particles are for med from a large numbers of minerals, e.g. alumina, silica and iron oxides, coated with sulfates, nitrates and organic species as small particles in the atmosphere. Mineral dust always acts like solid core for trace gases con- densation on their surface. Another important aspect of studying mineral aero sols in Antarctica is the need to interpret records of particulates observed in firn and ice cores. Mineral dust is one of the more studied paleoclimatic and paleo-environmental proxies among those that can be recovered from the ice cores. Dust particles arrive in the remote polar area after long-range transport from deserted and semi-deserted continental areas located at lower latitudes. Many characters of dust in the ice are measured, because of their potential to provide paleo-climatic information on the location and aridity at the dust sources, the scavenging and transport processes, and the atmospheric pathways. Although global dust sources are absent, Antarctica is the largest polar desert in the world, where appro- ximately 2% of its surface area is ice-free and contains active High Latitude Dust sources (HLD, Bullard et al., 2016). The best-known local dust sources are located in West Antarctica, with the McMurdo Dry Valleys being the largest ice free area (approximately 4,800 km2) with frequent dust suspension (Lancaster, 2002; Ayling and McGowan, 2006; Atkins and Dunbar, 2009; Bullard et al., 2016). As it follows from dust samples collected in snow pits on Berkner Island, the dust sources are located also in the ice-free areas of East Antarctica (Bory et al. 2010). Coastal ice-free areas have also been identified as active dust sources around the Maitri Station, Larsemann Hills, and Neumayer Station in East Antarctica (Weller et al., 2008; Chaubey et al., 2011; Bud havant et al., 2015), as well as in the Antarctic Peninsula region (Artaxo and Rabello, 1992; Kavan et al., 2017; Asmi et al., 2018). Alternately, the mineral particles can be re- sus pended from the surface of ablating glaciers (At- kins and Dunbar, 2009). Long-range transport of dust from other HLD sources, such as South America (Patagonia), New Zealand, and deserts in Australia and Africa, contribute to the dust depositions in Antarctica (Ne and Bertler, 2015; Bullard et al., 2016; Asmi et al., 2018). The main non-Antarctic dust source for the Antarctic Peninsula region is in Patagonia (Bullard et al., 2016). Patagonian dust was found in ice cores and snow samples in the Antarctic Peninsula and in East Antarctica (Basile et al., 1997; Pereira et al., 2004; McConnell et al., 2007; Bory et al., 2010; Delmonte et al., 2017). The dust deposition rates of > 100 g m–2 year–1 were reported from Patagonia (Bullard, 2016). The rates measured in McMurdo Dry Valleys (< 8 g m–2 year–1) are lower than other HLD sources (Lancaster, 2002). Nevertheless, the dust fluxes of 7.8—24.5 g m–2 year–1 (Atkins and Dunbar, 2009) and 0.2—55 g m–2 year–1 (Chewings et al. 2014) are reported in this source. The mass concentrations of PM 10 (particles with a diameter of < 10 μm) and PM 2.5 (with a diameter of < 2.5 μm) in boundary atmospheric layer were 5.1 and 4.3 mg m–3, respectively in the Larsemann Hills during summer (Budhavant et al., 2015), and 8.3 and 6.03 mg m–3 at the Maitri station (Chaubey et al., 2011). PM 10 concentrations from McMurdo station during two summers in 1995—1997 were 3.4 and 4.1 mg m–3 on average (Mazzera et al., 2001). Mean PM 10 and PM 2.5 concentrations of 4.4 mg m–3 and 2.4 mg m–3, respec tively were measured in the 5ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides Antarctic Peninsula during the late 1980s (Artaxo and Rabello, 1992). Seasonal variations in aerosol loadings showed increased concentrations in January and a decrease in February and March in Terra Nova Bay, West Antarctica in 2000—2001 (Truzzi et al., 2005). PM 10 concentrations of 2.1—5 mg m–3 on average were reported from the Antarctic Peninsula, with higher concentration in summer (October to March) in 2013—2015 (Asmi et al., 2018). The con- centrations of the particles near ly doubled in summer when winds were high (Asmi et al. 2018). Because mineral dust may undergo processing as it is transported in the atmosphere, its impact on global processes may change over the course of its “life story”. Therefore, knowledge of its physicochemical pro perties, especially its adsorption characteristics, is very important for predicting its effects in atmospheric chemistry and biogeochemical cycles in Antarctica. Most of the experiments on the interaction of trace gases with mineral dust were performed with oxides such as SiO 2 , Al 2 O 3 , and CaO (Pokrovskiy et al., 1999; Al-Abadleh and Grassian, 2003). The surface of mineral dust particles acts as a sink for many gases, such as sulfur dioxide (SO 2 ), with the formation of sulfite ion (SO 3 2–) associated with it, which is oxidized to sulfate ion (SO 4 2–) in the presence of ozone or other oxidizing agents. However, an evi- dence has recently been obtained of an alternative way of generating these ions for a series of reactions: in the presence of water vapor, titanium oxides, iron or mineral dust containing these oxides, exposure to the UV part of solar radiation produces gaseous sulfuric acid (H 2 SO 4 ), which then reacts with the surface of the particles (Dupart et al, 2012). Metal oxides in mineral dust act as atmospheric photocatalysts, pro- moting the formation of gaseous OH radicals, which initiate the conversion of SO 2 to H 2 SO 4 in the vicinity of the particle. At a low concentration of dust in the atmosphere characteristic over Antarctica, this process can lead to the nucleation phenomena and the for- mation of the CCN. In the present work, highly dispersed fumed silica, alumina, titania, and mixed X/SiO 2 oxides (X = = Al 2 O 3 , TiO 2 and Al 2 O 3 /TiO 2 ) are used as proxies of mineral aerosols. These oxides produced by conden- sa tion processes are often of more theoretical interest because it is easier to control their nucleation and growth rate, particle size and size distribution, and rate of disappearance. They can therefore be used more readily to study the various theories of aerosol formation and destruction. The choice of oxides SiO 2 and Al 2 O 3 is due to their dominance in the earth’s crust and in the composition of the mineral dust as ice nucleating particles, while TiO 2 has semiconductor properties and can serve as a natural photocatalyst for the formation of H 2 SO 4 , which is the main component of CCN that have a significant impact on the Antarctic climate. Natural analogues of these oxides can be mineral particles formed during volcanic eruptions, for example, Mt. Erebus in Antarctica, as a result of high-temperature hydrolysis of metal halides, MHal n (M = Si, Al, Ti; Hal = Cl, Br, I) in presence of water vapor. Nitrogen was used as an adsorbed substance. The main goal of the work was to determine the influence of the oxides composition on the adsorption characteristics of their surface. MATERIALS AND METHODS Highly dispersed fumed individual silica, alumina, titania and mixed oxides X/SiO 2 (X = Al 2 O 3 , TiO 2 , Al 2 O 3 /TiO 2 ) (synthesized at the experimental plant of the Institute of Surface Chemistry of the National Academy of Sciences of Ukraine, Kalush, Ukraine) were studied at various concentrations (C X ) phase X oxide (Table 1). Titania, titania/silica and alumina/ titania/silica contain a mixture of anatase (particle shell, main part) and rutile (core of particles). Alumina includes ≈ 20% (by weight) of the crystalline γ-phase and ≈ 80% of the amorphous phase, whereas in alu- mina/silica and alumina/titania/silica it is completely amorphous. Silica is completely amorphous in all fumed oxides. Alumina/titania/silica includes ≈ 22% Al 2 O 3 , ≈ 28% SiO 2 and ≈ 50% TiO 2 (a mixture of 88% anatase and 12% rutile). The phase composition and other properties of these mixed oxides are reported in (Gun’ko et al. 2007). The nitrogen adsorption/desorption isotherms on the oxide surfaces were measured at 77.35 K and relative pressure x = P/P S (P and P S are the equilibrium 6 ISSN 1727-7485. Ukrainian Antarctic Journal. 2019, № 1 (18) M. S. Bazylevska, V. I. Bogillo vapor pressure of nitrogen and its saturated vapor pressure, respectively) in the range from ≈ 5 × 10–7 to ≈ 0.99 by using an ASAP 2010 V-3.00 volumetric multigas sorption analyzer (Micromeritics, Norcross, GA). Before measurements, the samples were sub- jected to treating in vacuum at 393 K for 6 hours to remove physically adsorbed water and other volatile impurities from the surface of the oxides. The total pore volume was estimated by converting the volume adsor bed at the relative pressure of 0.985 to the volume of liquid nitrogen. Methods for the calculation of adsorption parameters BET theory The specific surface area of the samples was calculated in accordance with standard Brunauer – Emmett – Teller (BET) procedure based on adsorption data in the x = P/P S range from 0.06 to 0.25 (Brunauer et al., 1938; Gregg et al, 1982) (1) S BET = a m σ m N A (2) , (3) where a is the number of moles of adsorbed substan- ce per unit weight of adsorbent (mol g–1), a m is the capacity of the monolayer of adsorbed substance per unit weight of adsorbent, σ m is the average area occupied by the adsorbed molecule in the monolayer (for N 2 it is assumed to be 16.2 Å2), N A is the Avogadro number, ΔQ A is the average differential heat of ad- sorption, ΔQ V is the heat of vaporization of the ad- sorbed substance, R is the universal gas constant, T is the adsorption temperature in K. Regularization procedure The nitrogen adsorption in the monolayer taking into account the energetic heterogeneity of the oxide surface was studied using the modified regularization procedure proposed in (Pyziy et al., 1997; Bogillo and Shkilev, 1999). Using the capacities of the monolayer obtained by the BET method, a m , for those values of a for which a m ≥ a, we can determine the overall surface coverage with adsorbed substance within the monolayer, Θ(P,T) = a/a m . Adsorption within these limits is generally described by the Fredholm integral equation of the first kind , (4) where θ(P, T, E A ) is the coverage of the local surface area with the adsorption energy E A , ρ(E A ) is the normalized differential surface distribution on E A , E A(min) and E A(max) are the lower and upper limits of this distribution. In the simplest case, the local coverage, θ(P, T, E A ), is described by the Langmuir isotherm: , (5) where K L, 0 is a preexponential factor depending on the rotational, vibrational, and translational degrees of free- dom of a polyatomic molecule adsorbed on the sur face and in the gas phase. This value can be approximately estimated using the ratio (Bogillo et al., 1998) K L, 0 ≈ P s exp(ΔQ V / RT). (6) One of the important problems in describing ad sor- ption equilibria on a heterogeneous surface remains the choice of the minimum information necessary for a stable calculation of the distribution ρ(E A ). The main idea of the numerical regularization is to replace the ill-posed problem of minimizing the selected function by a well-posed problem which smoothes the calcu- la ted distribution and distorts the origin problem insignificantly. Thus, the solution of equation (4) is replaced by minimizing the functional: (7) . 7ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides where α (1 ≥ α > 0) is the regularization parameter depending on the relative errors in determining the adsorption isotherm. To obtain the optimal α, we proposed a two-step procedure. First, the functional Φ[ρ(E A )] is minimized at α = 0. Thus, this minimum can serve as an measure of the accuracy of experimental data for m points on the adsorption isotherm: ( ) 2/1 1 20 )(),,(),(1min ⎥ ⎦ ⎤ ⎢ ⎣ ⎡ −Θ= ∑ = m j AA EETPTP m ρθξ . In the second step, the value of α is calculated at which the distribution ρ1(E A ), which minimizes the func tional Φ[ρ(E A )], satisfies the following condition: (9) . A feature of this modified method is the possibili ty of improving the solution by varying the free parame- ter η. The calculations showed that none of the methods for estimating α proposed in the literature leads to stable solutions of equation (4) in the absence of η. The distributions ρ(E A ) were calculated on the basis of part of the nitrogen adsorption isotherms corresponding to the monolayer surface coverage. ZAI theory A new isotherm, so-called Zeta Adsorption Isotherm (ZAI) was recently derived to describe accurately the adsorption in the full range of P up to P S (Zandavi et al., 2014). This isotherm is obtained in the app- roximation of adsorbed vapor as a set of molecular clusters, of which at least one is adsorbed by one of the M adsorption sites. Each adsorbed cluster is approximated as a quantum-mechanical harmonic oscillator with a binding energy that depends on the number of molecules in the cluster. The maximum number of molecules which cluster can consist of is ζ m . Using the canonical ensemble, the dependence of the amount of adsorbed matter on the solid/vapor interface per unit surface on the vapor pressure ratio is described as . (10) Parameters c Z and α Z are related to distribution of the clusters with different number of molecules and to the chemical potential of the adsorbed liquid at standard pressure, respectively. In ZAI, the number of adsorption sites per unit of mass of a solid, M g is related to the specific surface area, A s , as M g = A s M. (11) In the derivation of ZAI, it is assumed that one molecular cluster occupies one adsorption site. The average cross-sectional area of the adsorption site or the molecular cluster of a given vapor (I) is denoted as σ(I). Then the specific adsorption surface area of the solid, A s is given as σ(I) M g (I) = A s . (12) When the specific volume of the adsorbed liquid film is equal to that for a pure liquid in the volume, v f , the thickness of the adsorbed liquid film, τ af , is defined as . (13) Equation 10 together with the Gibbs adsorption equation for this surface allows to derive the ratio for surface tension or free surface energy of a solid in the absence of adsorption, γS0 (Ghasemi et al., 2009): , (14) where γLV is the surface tension or free surface energy of the adsorbed substance in the liquid/vapor system and k B is the Boltzmann constant. Lifshitz theory The value of γ S0, in the general case, is the sum of the dispersive, γ S D and polar, γ S p components of the free surface energy: 8 ISSN 1727-7485. Ukrainian Antarctic Journal. 2019, № 1 (18) M. S. Bazylevska, V. I. Bogillo γS0 = γ S D + γ S p. (15) The dispersive component, γ S D is related to the Ha maker constant of the material, A H (Israelachvili, 1992): A H = 24πD 0 2γ S D, (16) where D 0 is the smallest equilibrium distance between two identical materials in a vacuum. Given the Born repulsion, this distance is 1.6 A. On the other hand, the approximate expression from the Lifshitz’ theory for A H in vacuum or in air can be written as (Dzyaloshinskii et al., 1961): , (17) where n 0 is the refractive index, ε k is the permitti- vity of the material, ν c is the main frequency of electron absorption in the UV range (ν c = (3÷5) × × 1015 s–1), and h is the Planck constant (h = 6.626 × × 10–34 J s). RESULTS AND DISCUSSION Fumed oxides, such as silica, titania, alumina, silica/ alumina, titania/silica, alumina/titania/silica are wi- de ly used in industry as adsorbents, pigments, catalysts, fillers and additives in polymers. There is a multistage hierarchy of the oxides structure related to the features of their synthesis when using MCl n (M = = Si, Ti, and Al) in an oxygen/hydrogen flame at T > 1300 K. Variations in the reaction temperature and the ratio between the O 2 /H 2 and MCl n concentrations affect the structural characteristics of the primary particles and the concentration of hydroxyl groups on the surface of the oxides. Nonporous spherical primary particles with a diameter of 5—100 nm, depending on the synthesis conditions and the composition of the oxides, form aggregates with a diameter of 100— 500 nm, and then loose agglomerates (>1 μm). These structural levels differ significantly in apparent density, ρ ap . For example, for fumed silica, ρap is 1—3% for agglomerates, ∼30% for aggregates, and ∼100% of the specific density of primary particles (Gun’ko et al., Table 1. The specific adsorption area of the oxides surface, S BET , the С constant of the BET equation, the nitrogen average isosteric adsorption heat, ΔQ A , the apparent pore volume, v p , the nitrogen average adsorption energy in the monolayer, E A(av) and its standard deviation, σ Ea Sample Composition S BET v p C ΔQ A E A(av) σ Ea m2g–1 cm3g–1 kJ mole–1 T 100 100% TiO 2 60 0.17 98 8.53 7.9 2.9 ST 29 SiO 2 -29%TiO 2 73 0.16 93 8.49 7.3 4.2 ST 20 SiO 2 -20%TiO 2 65 0.13 263 9.16 7.6 6.5 ST 14 SiO 2 -14%TiO 2 217 0.49 117 8.64 6.6 3.1 ST 9 SiO 2 -9%TiO 2 198 0.47 116 8.63 7.1 2.2 S 100 100%SiO 2 267 0.62 126 8.69 7.1 2.5 SA 1..3 SiO 2 -1.3%Al 2 O 3 294 0.68 129 8.70 7.7 1.6 SA 3 SiO 2 -3%Al 2 O 3 156 0.35 165 8.86 7.6 4.7 SA 23 SiO 2 -23%Al 2 O 3 311 0.74 106 8.58 7.4 1.6 SA 30 SiO 2 -30%Al 2 O 3 239 0.57 106 8.58 7.5 1.8 A 100 100%Al 2 O 3 159 0.42 133 8.72 7.3 1.5 SAT SiO 2 -22%Al 2 O 3 -50%TiO 2 32 0.08 97 8.52 6.9 8.3 9ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides 2007). The smaller these particles, the stronger they are bound in the aggregates and the narrower is the particle size distribution. Roughness and amorphisms of the particle surface, variations in the types and concentration of hydroxyl groups on the surface can be the main reasons for the structural and energetic heterogeneity of the oxides surface with respect to various adsorbates. Since some phases in mixed oxides are amorphous (SiO 2 , Al 2 O 3 ), while others, for example, TiO 2 , can be crystalline, their surface heterogeneity can increase. The interfaces between the amorphous and crystalline phases in such oxides include strained bonds, incompletely coordinated metal atoms (Lewis acid centers), single and bridged hydroxyl groups (Bronsted acid centers), strongly bonded water molecules, and other adsorption centers that cause high surface heterogeneity. One of the main characteristics of the adsorption capacity of materials is the specific adsorption surface area, S BET . The higher it is, the greater the substance amount is held by a unit weight of the adsorbent, i.e., the more efficient the adsorption. These S BET for the studied oxides are given in Table 1. It also presents the pore volumes of materials, v p , corresponding to the effective volume, since nitrogen adsorption occurs not only in the internal free volume of the aggregates, but also in the free volume of agglomerates, that is, on the outer surface of the aggregates. Fig. 1 shows the experimental isotherm of nitro- gen adsorption on the surface of mixed SAT oxide (Table 1) in the P/P S range from 0 to 1.0 (a) and up to 0.35 (b). Its shape corresponds to the type II adsorp- tion isotherm according to the Brunauer classification (Gregg et al., 1982), which is characteristic of vapor adsorption on the surface of non-porous materials. The absence of a plateau on the adsorption isotherms observed at P/P S > 0.9 (Fig. 1, a) and the lack of hysteresis, i. e. coincidence of the adsorption and desorption isotherms, testifies that mesopores con- tri bution in the total pore volume of the studied ma- terials is negligible. Fumed TiO 2 includes primary crystalline particles of anatase (70÷85%) and rutile (15÷30%), while fumed Al 2 O 3 ≈ 20% of its crystalline γ-form. Fumed SiO 2 is completely amorphous. Obviously, the observed dec- rea se in S BET during the transition from silica to tita nia/ silica and titania, as well as close S BET values for silica, silica/alumina and alumina are due to the contribution of crystalline forms of TiO 2 and Al 2 O 3 to S BET for mixed oxides. Low v p indicate the con den sation of adsorbed nitrogen in the secondary pores formed due to the interparticle space of the aggregates upon contact of the primary non-porous oxide particles. Fig. 1. Experimental and calculated according to the theories of ZAI and BET nitrogen adsorption isotherms on the surface of alumina/titania/silica (SAT) at 77.35 K in the P/P S range from 0 to 1.0 (a) and up to 0.35 (b) a b 10 ISSN 1727-7485. Ukrainian Antarctic Journal. 2019, № 1 (18) M. S. Bazylevska, V. I. Bogillo The average differential heats of nitrogen ad sorp- tion calculated on the basis of the C constant of the BET equation are given in Table 1. All of them are in a rather narrow range (8.52÷9.16 kJ mol–1), but ex- ce ed the heat of vaporization of nitrogen (5.58 kJ mol–1), which is usually equated to the non-specific contribution (dispersion interaction) to the adsorption energy. Such a difference may indicate a significant con tribution of the specific (quadrupole – dipole and/or quadrupole – ion) interaction of a quadrupole nitrogen molecule with polar single or bridging OH– surface groups or with coordination-unsaturated metal ions at the oxide phase boundary. Some distributions of the oxides surface on the N 2 adsorption energy in the monolayer range, which com puted by using the regularization procedure, are shown in Fig. 2, a, b. It is seen that the oxides surface is characterized by a high degree of heterogeneity with respect to N 2 adsorption, which manifests itself in the presence of several peaks in the distribution curves and their considerable width. Since the distributions allow only a qualitative comparison of them for the surface of various oxides, we approximated them with a Gaussian distribution. The average N 2 adsorption energies and their standard deviations are given in Table. 1. Note that ΔQ V for N 2 , which characterizes the ability of the dispersion interaction of N 2 with surface sites, is 5.4 kJ mol–1. The upper limits of the distributions significantly exceed this value, which may be due to the contribution of the electrostatic interaction of the quadrupole of N 2 molecule with OH group dipoles and ions of the oxide surface sites. The highest E A at Θ(p.T) → 0 (Fig. 2, a) and E A(av) + σ Ea (Table 1) are typical for TiO 2 , ST 29 , and SAT, in which the content of crystalline phases is maximum. As follows from Fig. 1, the BET isotherm is close to the experimental one at P/P S < 0.3, but deviates significantly from it at large P/P S . It is well known that the BET isotherm describes adsorption on the surface of non-porous materials only in a limited pressure range corresponding to the filling of the monolayer (Gregg et al., 1982). At P → P S , the BET equation predicts infinite adsorption and negative adsorption at P > P S . Other adsorption isotherms (Frenkel – Halsey – Hill or Aranovich – Donahue) more accurately describe adsorption at high P, but they also predict infinite adsorption at P ≈ P S . Then the Zeta Adsorption Isotherm (ZAI) used here to describe accurately the adsorption in the full range of P up to P S . Table 2 shows the specific surface areas of oxides, A s , their monolayer capacitances, M V and M g , Fig. 2. Distributions of surface of SiO 2 , TiO 2 , TiO 2 /SiO 2 , TiO 2 /Al 2 O 3 /SiO 2 (a) and SiO 2 , Al 2 O 3 , Al 2 O 3 /SiO 2 (b) on the N 2 adsorp- tion energy 11ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides Table 2. The specific adsorption area of the oxides surface. A s , the monolayer capacities. M V and M g , the α Z , c Z and ζ m parameters of Eq. 10, and the square of the correlation coefficient for the Eq. 10, R2 Sample A s , m2 g–1 M V , cm3 g–1 M g × 106, mole g–1 α Z с Z ζ m R2 T 100 43 9,98 445 0,916 6137 70 0,955 ST 29 60 13,76 614 0,862 1167 72 0,947 ST 20 51 11,68 521 0,862 3096 62 0,946 ST 14 176 40,36 1801 0,874 1239 58 0,966 ST 9 159 36,43 1625 0,881 1059 54 0,970 S 100 204 46,86 2091 0,885 1650 71 0,963 SA 1..3 225 51,69 2306 0,887 1833 56 0,959 SA 3 116 26,60 1187 0,882 2053 61 0,956 SA 23 240 55,17 2461 0,887 1305 72 0,959 SA 30 184 42,23 1884 0,886 1205 59 0,962 A 100 123 28,13 1255 0,901 3483 59 0,963 SAT 223 5,24 234 0,897 1954 112 0,933 Table 3. The thickness of adsorbed N 2 film on the oxides surface, τ af , the free surface energy of the oxides in the absence of adsorption, γS0, this energy, estimated for mixed oxides, γS0 (calc) , the dispersive component of free surface energy of the oxides determined by immersion calorimetry, γD (exp) , by method of inverse gas chromatography at finite concentrations, γD (IGC) , and calculated by the Lifshitz’ theory, γD (calc) , the refractive indices, n 0 and permittivity, ε k of individual oxides Sample τ af γ S0 γ S0 (сalс) aγD (expp) bγD (calc) cγD (IGC) n 0 ε k nm mJ m–2 T 100 25 81,8 72 79 35,2 2,8 21,3 ST 29 26 67,3 74 ST 20 22 73,7 73 44,9 ST 14 21 68,3 73 ST 9 19 67,7 72 S 100 25 70,9 32 34 28,6 1,5 4,6 SA 1..3 20 71,7 71 SA 3 22 72,1 71 SA 23 26 69,5 72 SA 30 21 68,9 73 32,5 A 100 21 76,9 85 80 51,8 1,8 10,4 SAT 40 72,8 78 a from the calorimetric data of the immersion of oxides in n-heptane (Medout-Marere, 2000). b based on the Hamaker constants calculated by the Lifshitz theory (Bergstrom, 1997). c from data of inverse gas chromatography at finite concentrations (Bogillo et al., 1996). 12 ISSN 1727-7485. Ukrainian Antarctic Journal. 2019, № 1 (18) M. S. Bazylevska, V. I. Bogillo the parameters of Eq. 10, and the squares of the co- rrelation coefficients. As follows from Fig. 1, a, the isotherm calculated by the ZAI equation deviates noticeably from expe- rimental one in the range 0 < x < 0.35, but it is close to the experimental one in the range 0.35 < x < 0.99, while the isotherm calculated by the BET equation deviates significantly from it and a → ∞ as x → 1.0. Using the σ(N 2 ) = 16.2 Å2 for the surfaces of all oxides, the M equals to M g /A s = 1.0244 × 10–5 mole m–2. A comparison of the A s values with the S BET from Table 1 indicates a close relationship between them: A s = (0.775 ± 0.012) · S BET ; R2 = 0.999. The lower surface areas obtained using ZAI compared to BET may be due to variations in the orientation of nitro- gen molecules (e.g., orthogonal) in clusters (ZAI), in contrast to the strictly parallel orientation of mo le cu- les in the adsorbed layer, as is assumed in the classical BET theory. The Table 3 shows the thicknesses of the adsorbed nitrogen film on the oxide surface, the free surface energies of these oxides in the absence of adsorption, these energies estimated for mixed oxides based on γ S0 for component X in the oxide, γ S0 (calc) , dispersive components of the free surface energy of individual oxides, determined by the calorimetric method, γD (exp) and by the method of inverse gas chromatography at final concentrations, γD (IGC) , calculated using Lifshitz’ theory, γD (calc) , as well as refractive indices, n 0 and permittivity, ε k of individual oxides. In the calculations for nitrogen at 71.1 K, γLV = 10.3 mJ m–2 was used (Prausnitz, 1966). We estimated γ S0 for mixed oxides based on these values for individual oxides and the fraction of component X. As can be seen from the data in Table 3, for most mixed oxides, the calculated γ S0 exceed the experimental ones by 2.5–6.7 mJ m–2. Only for samples ST 20 , SA 1,3 , and SA 3 there is a slight excess (by 0.7÷1.1 mJ m–2) of experimental values over the calculated ones. The assumed additivity of γ S0 for mixed oxides is valid for an external mixture of oxides forming par ti- cles, while for an internal mixture that is inhomo ge- neous in volume of a particle, it will be violated. Among the studied individual oxides, silica has a mi ni mum γ S0 and is part of all mixed oxides. There- fore, we can assume a higher SiO 2 content in the upper shell of mixed oxide particles compared to its bulk content, while Al 2 O 3 and crystalline TiO 2 pha- ses form mainly the core of these particles. This assumption is consistent with the conclusions about the particle structure of fumed mixed oxides in (Gun’ko et al., 2007). Square root of free surface energy of oxides as a function of the average nitrogen adsorption energy within the monolayer is shown in Fig. 3. An increase in E A(av) leads to an increase in (γS0)1/2, and a linear relationship is observed between these parameters: ; R = 0.523. Thus, using Eqs 16 and 17, we can estimate γ S D of the material. The values of n 0 and ε k for indivi- dual oxides are given in the Table 3. The calculated γ S D (calc) values (in mJ m–2) are varied in sequence: TiO 2 (216) > Al 2 O 3 (70) > SiO 2 (33), which qualitatively coincides with the sequence of changes in γ S0 of these oxides (TiO 2 (82) > Al 2 O 3 (77) > SiO 2 (71)). Using A H calculated ta king into account various spectral corrections from (Bergstrom, 1997), lower γ S D values for TiO 2 (77÷82 mJ m–2) are obtained, which are Fig. 3. The surface free energy of the individual and mixed Si, Ti and Al oxides as a function of their average N 2 adsorption energy within the monolayer 13ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides close to those found for Al 2 O 3 (69÷72 mJ m–2), however for SiO 2 in all cases, the calculation leads to lower γ S D (27÷31 mJ m–2). Plots of A H for inorganic materials from (Bergst- rom, 1997) and γS0 for the oxides on n 0 and (ε k )1/2 values are shown in Fig. 4. It can be seen that in all cases there is a tendency for A H and γS0 to increase as the n 0 and (ε k )1/2 rise. The relations (A H × 10–20 = = (14.1 ± 1.6)n 0 – (13.5 ± 3.1), N = 30, R = 0.854 and A H × 10–20 = (7.2 ± 1.8) (ε k )1/2 – (8.3 ± 5.1), N = = 30, R = 0.636) allow to estimate easy the A H values of materials. The γ S D value based on A H determined by ca lo ri- metric immersion of metal oxides in n-hexane (Me dout-Marere, 2000) is shown in Table 3. It is seen that, in contrast to the calculated γ S D and experimental γS0, the reverse sequence of oxide activity (Al 2 O 3 > TiO 2 ) is observed, however, lower γ S D is obtained for SiO 2 , which is close to that calculated using the equations of the Lifshitz theory. The Table 3 shows also γ S D determined from data of inverse gas chromatography at finite concentrations at 403 K (Bogillo et al., 1996). As in previous case, γ S D Fig. 4. The dependence of Hamaker constant for inorganic materials (a, b) and free surface energy of the metal oxides in the absence of adsorption (c, d) on the index of refraction (a, c) and on the square root of permittivity of the materials (b, d) 14 ISSN 1727-7485. Ukrainian Antarctic Journal. 2019, № 1 (18) M. S. Bazylevska, V. I. Bogillo for SiO 2 is lower than for other oxides and for Al 2 O 3 γ S D is higher than for TiO 2 . If for SA 30 , γ S D is between γ S D of individual SiO 2 and Al 2 O 3 , then γ S D for ST 20 is significantly higher than that obtained for indi vidual Si and Ti oxides. For the same oxide, the highest constant С of the BET equation (263) is observed (Table 1) compared with other oxides (93÷165) and, accordingly, the highest isosteric heat of adsorption, ΔQ A (9.2 kJ mole–1) in compared with the rest oxides (8.5÷8.9 kJ mole–1). The comparison of γ S D and γS0 values for various silicas (Bilinski et al., 1999; Pokrovskiy et al., 1999) shows that these values depend on the method used, the temperature of preliminary sample preparation, the nature of the adsorbed substance, the adsorption temperature, and γ S D varies from 28.6 to 71 mJ m–2 (Bilinski et al., 1999), which coincides with γ S D (IGC) and γS0 values from the Table 3. Even greater variations are observed for γ S p (11.9÷160 mJ m–2), which is associated with a significant influence of the choice of a polar adsorbed substance for de- termining this parameter (Bilinski et al., 1999). Si- milar significant variations in γ S D (IGC) and γS0 were also noted for other oxides, minerals, carbon and solid organic materials (Pokrovskiy et al., 1999). Slight variations of γS0 for the studied oxides, in contrast to the calculated and ex perimental γ S D and the dependencies shown in Fig. 4, c, d suggest that the main contribution to γS0 is made by its dispersive component. The obtained parameters for the metal oxides allow evaluating the adsorption activity of their surface with respect to other trace gases in the Antarctic atmosphere. For these parameters it is necessary to calculate the partition coefficients of these gases between particles and the atmosphere, K SA , and the kinetics of their removal from the atmosphere (Bogillo et al., 2008). The K SA value for the adsorbed substance/material surface pair can be calculated by knowing the specific surface area of the material, its free surface energy, or the Hamaker’ constant, as well as the γLV value (Bogillo et al., 1998; Pokrovskiy et al., 1999), or the critical temperatu - re and critical pressure of the adsorbed substance (Mauer et al., 2001). CONCLUSIONS Using the volumetric method, low-temperature nit- rogen adsorption isotherms on the surface of 12 fumed individual and mixed oxides of Si, Ti, and Al, as components of mineral aerosols in the Antarctic atmosphere, were measured. The aim of the work was to determine the effect of the origin and concentration of X, C X in oxides of the X/SiO 2 type (X = Al 2 O 3 , TiO 2 , Al 2 O 3 /TiO 2 ) on the structural and energetic characteristics of their surface. Using the BET theory, the specific surface areas of the oxides, S BET , were calculated. The relationship between C X and S BET for mixed oxides does not exist. Since the synthesis of oxides is carried out by hyd- rolysis of metal chlorides MCl n (M = Si, Ti, and Al) in an oxygen/hydrogen flame at T > 1300 K, variations in T and the concentrations of O 2 , H 2 , and MCl n , as well as the degree of crystallinity, probably significantly affect structural characteristics of primary par ticles and aggregates formed from them. Using the regularization method, the surface dis- tri butions of the oxides on the N 2 adsorption energies were computed. It was found that their surface is cha racterized by a high degree of heterogeneity, manifested in the presence of several peaks in the distribution curves and their significant width. Since the upper limits of the distributions significantly exceed the heat of vaporization of N 2 , this may be due to the significant contribution of the electrostatic interaction between the quadrupole molecule N 2 and dipoles of surface OH groups and ions in the overall adsorption energy. Since the BET isotherm describes adsorption only in a limited narrow pressure range, the Zeta Adsorp- tion Isotherm (ZAI) derived in the approximation of adsorbed vapor as a set of molecular clusters was used for its full range. ZAI describes isotherms well, and the specific surface areas of oxides, A s , the maxi mum number of molecules in adsorbed clusters, the thick- ness of an adsorbed liquid film, and the free surface energies of oxides in the absence of adsorption, γS0, are calculated using the ZAI equations. The A s correlates well with S BET and account for 77.5% of one, which may be due to the contribution 15ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides of the orthogonal orientation of N 2 molecules in clusters (ZAI), in contrast to their parallel orientation in the BET theory. It was shown that γS0 increase with rise of average adsorption energies of N 2 . There is no dependence between γS0 and C X (taking into account γS0 for X) for mixed oxides, which may be due to a higher content of SiO 2 in the shell of their particles, while Al 2 O 3 and TiO 2 form mainly their core. The γS0 value of individual oxides increases with rise of their permittivity and refractive index. The γS0 is in the range of dispersive components of the free surface energy determined by other experimental methods and calculated according to the Lifshitz theory. These parameters for oxides make it possible to estimate the adsorption activity of their surface in relation to other trace gases in the Antarctic atmo- sphere, which is necessary to evaluate their partition coefficients between particles and the atmosphere and their removal kinetics. Acknowledgements. Adsorption measurements were performed at the Adsorption and Chromatography Laboratory (Head is Prof. M. Jaroniec) of the Che- mistry Department, Kent State University, Ohio, USA with financial support from the US National Science Foundation (COBASE program). REFERENCES 1. Al-Abadleh, H. A., Grassian, V. H. 2003. Oxide surfaces as environmental interfaces. Surface Science Reports, 52. 63–161. 2. Artaxo, P., Rabello, M. L. C. 1992. Trace elements and in dividual particle analysis of atmospheric aerosols from the Antarctic Peninsula. Tellus B., 44. 318—334. 3. Asmi, E., Neitola, K., Teinilä, K., Rodriguez, E., Virk- ku la, A., Backman, J., et al. 2018. Primary sources control the variability of aerosol optical properties in the Antarctic Peninsula. Tellus B., 70:1414571. doi:10.1080/16000889. 2017.1414571. 4. Atkins, C. B., Dunbar, G. B. 2009. Aeolian sediment flux from sea ice into southern McMurdo sound, Antarctica. Global Planetary Change, 69. 133—141. 5. Ayling, B. F., McGowan, H. A. 2006. Niveo-eolian se- diment deposits in coastal South Victoria Land, An tar- ctica: indicators of regional variability in weather and climate. Arctic, Antarctic and Alpine Research, 38. 313— 324. 6. Basile, I., Grousset, F. E., Revel, M., Petit, J. R., Biscaye, P. E., Barkov, N. I. 1997. Patagonian origin of glacial dust deposited in East Antarctica (Vostok and Dome C) during glacial stages 2, 4 and 6. Earth Planet Science Letters, 146. 573—589. 7. Bergstrom, L. 1997. Hamaker Constants of Inorganic Ma terials. Advances in Colloid and Interface Science, 70. 125—169. 8. Bilinski, B.. Holysz, L. 1999. Some Theoretical and Ex- pe rimental Limitations in the Determination of Surface Free Energy of Siliceous Solids. Powder Technology, 102. 120—126. 9. Bogillo, V. I., Shkilev, V. P., Voelkel A. 1996. Chemical Heterogeneity of Metal Oxides Surface as Studied by Inverse Gas Chromatography at Finite Concentrations. Adsorption Science and Technology, 14(3). 189—198. 10. Bogillo, V. I., Shkilev, V. P., Voelkel, A. 1998. Determination of Surface Free Energy Components for Heterogeneous Solids by Means of Inverse Gas Chro- matography at Finite Concentrations. Journal of Materials Chemistry, 8(9). 1953—1961. 11. Bogillo, V. I., Shkilev, V. P. 1999. Evaluation of Desorption Energy Distributions from TPD Spectra on the Hetero- geneous Solid Surfaces. Journal of Thermal Analysis and Calorimetry, 55(2). 483—492. 12. Bogillo, V. I., Bazylevska, M. S. 2008. Partitioning and Ex change of Organochlorine Contaminants between Abio tic Compartments in Antarctica. In Mehmetli E. et al (eds). The Fate of Persistent Organic Pollutants in the En vironment, Dordrecht: Springer. 333—351. 13. Bory, A., Wolff, E., Mulvaney, R., Jagoutz, E., Wegner, A., Ruth, U., et al. 2010. Multiple sources supply eolian mi- ne ral dust to the Atlantic sector of coastal Antarctica: evi- dence from recent snow layers at the top of Berkner Island ice sheet. Earth Planet Science. Letters, 291. 138—148. 14. Brunauer, S. Emmett, P. H., Teller, E. 1938. Adsorption of Gases in Multimolecular Layers. Journal of American Chemical Society, 60. 309—319. 15. Budhavant, K., Safi, P. D., Rao, P. S. P. 2015. Sources and elemental composition of summer aerosols in the Larsemann Hills (Antarctica). Environmental Science and Pollution Research, 22. 2041—2050. 16. Bullard, J. E., Baddock, M., Bradwell, T., Crusius, J., Darlington, E., Gaiero, D., et al. 2016. High-latitude dust in the Earth system. Review of Geophysics, 54. 447— 485. 17. Chaubey, J. P., Moorthy, K. K., Babu, S. S., Nair, V. S. 2011. The optical and physical properties of atmospheric aerosols over the Indian Antarctic stations during southern hemispheric summer of the international Polar Year 2007–2008. Annals of Geophysics, 29. 109—121. 18. Chewings, J. M., Atkins, C., Dunbar, G., Golledge, N. R. 2014. Aeolian sediment transport and deposition in a 16 ISSN 1727-7485. Ukrainian Antarctic Journal. 2019, № 1 (18) M. S. Bazylevska, V. I. Bogillo modern high-latitude glacial marine environment. Se- dimentology, 61. 1535—1557. 19. Delmonte, B., Paleari, C. I., Andò, S., Garzanti, E., An- dersson, P. S., Petit, J. R., et al. 2017. Causes of dust size variability in central East Antarctica (Dome B): atmo- spheric transport from expanded South American sources during marine isotope stage 2. Quaternary Science Review, 168. 55—68. 20. Dupart, Y., King, S. M., Nekat, B., Nowak, A., Wie- densohler, A., Herrmann, H., David, G., Thomas, B., Miffre, A., Rairoux, P., D’Anna, B., George, C. 2012. Mineral Dust Photochemistry Induces Nucleation Events in the Presence of SO 2 . Proceedings of National Academy of Sciences of USA, 109(51). 20842—20847. 21. Dzyaloshinskii, I.E., Lifshitz, E.M., Pitaevskii, L.P. 1961. The General Theory of Van der Waals Forces. Advances in Physics, 10. 165—209. 22. Ghasemi, H., Ward, C. A. 2009. Determination of the Surface Tension of Solids in the Absence of Adsorption. Journal of Physical Chemistry, 113. 12632—12634. 23. Gregg, S. J., Sing, K. S. V. 1982. Adsorption. Surface Area and Porosity, London. New York: Academic Press Inc. 24. Gun’ko, V. M., Blitz, J. P., Gude, K., Zarko, V. I., Gon- cha ruk, E. V., Nychiporuk, Y. M. Leboda, R., Sku- biszewska-Zieba, J., Osovskii, V. D., Ptushinskii, Y. G., Mishchuk, O. A., Pakhovchishin, S. V., Gorbik, P. P. 2007. Surface Structure and Properties of Mixed Fumed Oxides. Journal of Colloid and Interface Science, 314(1). 119—130. 25. Israelachvili, J.N. 1992. Adhesion Forces between Sur- faces in Liquids and Condensable Vapours. Surface Scien- ce Reports, (14). 109—159. 26. Kavan, J., Ondruch, J., Nývlt, D., Hrbá¡cek, F., Carri- vick, J. L., Láska, K. 2017. Seasonal hydrological and suspen ded sediment transport dynamics in proglacial strea ms, Ja mes Ross Island, Antarctica. Geography An nals, 99. 38—55. 27. Lancaster, N. 2002. Flux of eolian sediment in the McMur- do Dry Valleys, Antarctica: a preliminary assess ment. Arctic, Antarctic and Alpine Research, 34. 318—323. 28. Mauer, S., Mersmann, A., Peukert, W. 2001. Henry Coe- fficients of Adsorption Predicted from Solid Hama ker Constants. Chemical Engineering Science, 56. 3443—3453. 29. Mazzera, D. M., Lowenthal, D., Chow, J. C., Watson, J. G., Grubisic, V. 2001. PM 10 measurements at McMurdo station, Antarctica. Atmospheric Environment, 35. 1891— 1902. 30. McConnell, J. R., Aristarain, A. J., Banta, J. R., Edwards, P. R., Simoes, J. C. 2007. 20th-Century doubling in dust archived in an Antarctic peninsula ice core parallels climate change and desertification in South America. Proceedings of National Academy of Sciences of U. S. A., 104. 5743—5748. 31. Medout-Marere, V. 2000. A Simple Experimental Way of Measuring the Hamaker Constant A 11 of Divided Solids by Immersion Calorimetry in Apolar Liquids. Journal of Colloid and Interface Science, 228. 434—437. 32. Ne, P. D., Bertler, N. A. N. 2015. Trajectory modeling of modern dust transport to the Southern Ocean and An- tarctica. Journal of Geophysics Research Atmosphere, 120. 9303—9322. 33. Pereira, K. C. D., Evangelista, H., Pereira, E. B., Simo es, J. C., Johnson, E., Melo, L. R. 2004. Transport of crustal microparticles from chilean Patagonia to the An tarctic peninsula by SEM-EDS analysis. Tellus B., 56. 262—275. 34. Pokrovskiy, V. A., Bogillo, V. I., Dabrowski, A. 1999. Adsorption and Chemisorption of Organic Pollutants on the Solid Aerosols Surface. In. Dabrowski A. (ed). Adsorp- tion and its Application in Industry and Environmental Pro- tection. Amsterdam: Elsevier. 571—634. 35. Prausnitz, J. M. 1966. Surface Tension of Simple Liquids. Transactions of Faraday Society, 62. 1097—1104. 36. Pyziy, A. M., Volcov, V. B., Poznayeva, O. A., Bogillo, V. I. Shkilev, V. P. 1997. Comparison of Various Numerical Pro cedures for Analysis of Structural Heterogeneity. Langmuir, 13(5). 1303—1306. 37. Seinfeld, J.H., Pandis, S. N. 2006. Atmospheric Chemistry and Physics: From Air Pollution to Climate Change, Lon- don, New York: John Wiley & Sons, Inc. 38. Truzzi, C., Lambertucci, L., Illuminati, S., Annibaldi, A., Scarponi, G. 2005. Direct gravimetric measurements of the mass of the Antarctic aerosol collected by high volume sampler: PM 10 summer seasonal variation at Terra Nova Bay. Annals of Chemistry, 95. 867—876. 39. Weller, R., Wöltjen, J., Piel C., Resenberg, R., Wagenbach, D., König-Langlo, G., et al. 2008. Seasonal variability of crustal and marine trace elements in the aerosol at Neumayer station, Antarctica. Tellus B., 60. 742—752. 40. Zandavi, S. H. Ward, C. A. 2014. Clusters in the Adsor- ba tes of Vapours and Gases: Zeta Isotherm Approach. Physical Chemistry and Chemical Physics, 16. 10979—10989. 17ISSN 1727-7485. Український антарктичний журнал. 2019, № 1 (18) Adsorption properties of the fumed individual and mixed Si, Ti and Al oxides М. С. Базилевська*, В. Й. Богилло Інститут геологічних наук, Національна академія наук України, вул. Олеся Гончара, 55Б, м. Київ, 01054, Україна * Автор для кореспонденції: bazilevskaya1955@gmail.com АДСОРБЦІЙНІ ВЛАСТИВОСТІ ПІРОГЕННИХ ІНДИВІДУАЛЬНИХ І ЗМІШАНИХ ОКСИДІВ SI, TI ТА AL ЯК МОДЕЛЕЙ МІНЕРАЛЬНИХ АЕРОЗОЛІВ В АТМОСФЕРІ АНТАРКТИКИ РЕФЕРАТ. Метою роботи було визначення впливу природи та вмісту X, C X в оксидах X/SiO 2 (X = Al 2 O 3 , TiO 2 , Al 2 O 3 / TiO 2 ) на характеристики їх поверхні. Методом волюметрії виміряні низькотемпературні ізотерми адсорбції азоту на поверхні 12 індивідуальних і змішаних пірогених оксидів Si, Ti та Al, як компонентів мінеральних аерозолів в атмосфері Антарктики. Згідно теорії БЕТ розраховано питомі площі поверхні оксидів, S BET . Залежності між C X і S BET для змішаних оксидів не виявлено, що пов’язано з впливом температури реакції гідролізу MCl n (M = Si, Ti та Al) у кисень/водневому полум’ї та відношень концентрацій O 2 , H 2 і MCl n на структурні характеристики первинних частинок та агрегатів. Методом регуляризації розраховано розподіли поверхні оксидів за енергіями адсорбції N 2 та показано, що вона характеризується високою мірою енергетичної неоднорідності. Для опису адсорбції N 2 у повному діапазоні його тисків застосовано Зета – ізотерму адсорбції (ZAI), яку отримано в наближенні адсорбованого пару, як набору кластерів молекул. За рівняннями ZAI розраховано питомі площі поверхні оксидів, A s , максимальні кількості молекул в адсорбованих кластерах, товщини адсорбованої рідкої плівки та вільні поверхневі енергії оксидів за відсутності адсорбції, γS0. A s гарно корелює з S BET та складає 77,5% від неї. Величина γS0 зростає при збільшенні середньої енергії адсорбції N 2 . Залежності між γS0 та C X (з урахуванням γS0 для X) для змішаних оксидів не виявлено. Для SiO 2 , Al 2 O 3 і TiO 2 γS0 зростає при збільшенні діелектричної проникності оксидів та показника заломлення і знаходяться в діапазоні їх дисперсійних компонент вільної поверхневої енергії, які визначено іншими експериментальними методами та розраховано згідно теорії Ліфшиця. Знайдені параметри для оксидів дозволяють оцінити активність їх поверхонь по відношенню до домішок в атмосфері Антарктики, що необхідно для розрахунку їх коефіцієнтів розподілу між частинками та атмосферою і кінетики їх видалення. Ключові слова: мінеральні аерозолі, атмосфера Антарктики, пірогенні індивідуальні та змішані оксиди Si, Ti та Al, адсорбція азоту.