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Distribution of Total Sulfur in Acidic, Basic and Neutral Fractions on Brazilian Asphalt Cements and its Relationship to the Aging Process Leandro M. de Carvalho, Paulo C. do Nascimento, Denise Bohrer, Luis E. Claussen, Luis Ferraz, Carla Grassmann, Hugo T. S. Braibante, Daiane Dias, Margareth Cravo, and Leni F. Mathias Leite Energy Fuels, Just Accepted Manuscript • DOI: 10.1021/ef5025643 • Publication Date (Web): 24 Feb 2015 Downloaded from http://pubs.acs.org on February 28, 2015
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Energy & Fuels
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Distribution of Total Sulfur in Acidic, Basic and Neutral Fractions on
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Brazilian Asphalt Cements and its Relationship to the Aging Process
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Leandro M. de Carvalho*a, Paulo C. do Nascimentoa, Denise Bohrera, Luís E. Claussena, Luis Ferraza,
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Carla Grassmann a, Hugo T. S. Braibantea, Daiane Diasb, Margareth Cravoc and Leni F. M. Leitec
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a
8
Brazil
9
b
10
c
11
PETROBRAS, Rio de Janeiro, RJ, Brazil
Departamento de Química, Universidade Federal de Santa Maria, 97110-970, CP 5051, Santa Maria, RS,
Departamento de Química, Universidade Federal do Rio Grande, Rio Grande, RS, Brazil Centro de Pesquisas e Desenvolvimento “Leopoldo Américo Miguez de Mello” (CENPES),
12 13 14 15 16
AUTHOR INFORMATION:
17
Phone/FAX: +55-32208870. E-mail:
[email protected] 18 19
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ABSTRACT: In this work, studies were performed in Brazilian asphaltic cements by
22
separating fractions of maltenes and asphaltenes using non-aqueous ion exchange liquid
23
chromatography (NIELC). Initially, three different aging processes (RTFOT, PAV and
24
SUNTEST) were applied to 23 different asphaltic cements for evaluating the changing of
25
asphaltenic (12.7±2.5 %) and maltenic
26
process was studied in a comparative way for 5 asphalt cements samples, since it caused the more
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pronounced changes in maltenes and asphaltenes among the asphaltic cements supplied by
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different Brazilian refineries. Asphaltenes presented the highest amount of polar compounds in all
29
the studied samples, herein attributed to compounds of acidic and basic character that contain
30
sulfur. It was also found that the aging of asphalt cement leads to an increase of the more reactive
31
acidic (9.5−18.9%) and basic (14.6−30.9%) fraction in both asphaltenes and maltenes. As a result,
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a reactivity index (Ir) for asphaltic cements was calculated and proposed for classifying the studied
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samples regarding their aging susceptibility. It was also observed that the less reactive asphaltic
34
cement presented the highest amount (>80%) of neutral sulfur compounds in maltenic fraction.
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Lastly, it was concluded that a higher content of total sulfur in asphalts does not imply necessarily
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in a higher chemical reactivity (susceptibility to aging) of the cement, as observed for 5 studied
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samples having total sulfur ranging from 1.8 to 3.4% (w/w). The presence of functional groups
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related to their specific heteroatoms, such as sulfur, suggest a possible way to explain a greater or
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lesser susceptibility of asphalts to aging.
(90.6±5.0 %) compounds. The RTFOT+SUNTEST
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Keywords: Asphalt cements; total sulfur distribution; aging processes, SUNTEST, reactivity
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index.
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1.
INTRODUCTION
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The speciation of sulfur in asphalt cements has becoming an important issue from
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scientific and technological viewpoints, since sulfur compounds are considered precursors of
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asphalt oxidation reactions. In this context, it is already known that changes in the
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physicochemical and rheological properties of asphalt cements are caused mainly by alteration in
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the chemistry of sulfured functional groups, the viscosity and the balance of polar/nonpolar
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groups.1 Among the processes involved in the asphalt aging, oxidation is considered the most
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significant one, since it takes place during the application of the wearing course and continues
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slowly during its pavement service.2 Beyond the formation of oxygenated compounds, the polar
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groups present in the asphalt cement tend to associate, forming micelles and agglomerates of high
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molecular weight and higher viscosity (asphaltenes).
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It is well known that oxidation processes in asphalts involve mainly the heteroatom sulfur
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by oxidation of e.g. sulfides to sulfoxides.1,2 Beyond oxidation processes involving sulfur
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compounds, carbonyl formation associated to e.g. naphthenes are involved in the chemical
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transformations taking place during asphalt aging.1 Chemical transformation of polar fractions in
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asphalts involve also the formation of ketones and alcohols concurrently with sulfoxides, being
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alcohols the main contributors to oxidative aging of asphalts with high content of sulfur.3
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Furthermore, ketones are formed primarily from the oxidation of benzyl carbons in side chains
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attached to highly condensed aromatic ring systems, which exist largely in the polar aromatics
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fraction of asphalts.4,5 Beyond the organic compounds containing basically sulfur, nitrogen and
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oxygen as heteroatoms, metallorganic compounds, such as vanadyl porphyrins, have been also
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described for asphaltic matrices and are also involved in the aging processes.6,7
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In this context, chemical transformations involving specific classes of sulfur compounds,
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such as thiophenes, sulfides, sulfoxides and sulfones of acidic, basic and neutral character were
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studied by Green, Payzant and co-workers.8−13 According to these work, there is a distribution of
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species according to their acid-base character in each respective class of sulfur compounds. These
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species characterize the more polar and, consequently, more reactive fraction of asphalt cements
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and can be directly involved in the aging mechanism. However, the understanding of the
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mechanisms associated with specific sulfur classes and their transformations during the aging has
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been investigated so little depth up to date.
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Speciation studies of sulfur compounds in asphalt have been described in the literature for
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asphaltic matrices produced in different countries.8−13 Although Brazil is one of the important
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producers of petroleum and petroleum-derived products worldwide, systematic studies focused on
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the physicochemical characterization of the asphalt cements produced in the refineries spread over
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the country have not been performed in depth up to date. Furthermore, the knowledge of sulfur
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species as markers of aging and quality indicators of asphalt cement is highly relevant, since it can
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contribute to establishing of criteria for the production of more resistant asphaltic mixtures and
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their additives as well.
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The aging process of asphalt cements have been evaluated by different analytical methods,
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which use techniques merely for specification studies or elucidation/understanding of the asphalt
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cement behavior. A typical method used for the characterization of asphalt cements is the liquid
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chromatography using silica columns (IATROSCAN), which identifies and quantifies the more
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generic chemical fractions (SARA: Saturates, Aromatics, Resins and Asphaltenes). Gel
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permeation chromatography (GPC) is used for separating the compounds according to the
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apparent molecular weight and the infrared spectroscopy (FTIR) identifies some functional groups
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(e.g. carbonyls and sulfoxides) formed after oxidation.14−17 Atomic force microscopy (AFM) has
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been recently applied to studies of physical properties of asphalts submitted to aging processes.18,
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In this work, studies were performed in asphalt cements by separating different fractions in
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order to understand their formation, especially regarding sulfur compounds. Initially, the
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separation of virgin asphalt cements was carried out for asphaltenes and maltenes by using the
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method described in ASTM D 4124.20 The next step consisted in a second fractionation, where
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both maltenes as asphaltenes were separated into acidic, basic and neutral fractions. For this
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purpose, the method described by Green and co-workers9 was adapted and applied to samples of
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Brazilian asphalt cements. The separations based on both the mentioned methods were made
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comparatively for virgin and aged asphalt cements. Thus, total sulfur was determined in the acidic,
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basic, and neutral asphalt fractions submitted to the different aging processes. Thus, the
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distribution of the compound classes in asphaltenic and maltenic fractions was obtained. The
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distribution profile for these compound classes was observed in asphaltenes and maltenes, which
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gave information on chemical transformations occurring during the aging process of asphalt
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cements. Considering the studied total sulfur distribution, a reactivity index (Ir) for 5 different
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asphaltic cements was calculated and proposed for classifying the studied samples regarding their
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aging susceptibility.
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2.
EXPERIMENTAL SECTION
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2.1 Instrumentation and Apparatus
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All asphalt cement samples were heated at 100 ° C for 60 minutes in an oven provided of
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air circulation (Q314 M - Quimis) before sampling the matrix for separations in order to keep the
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sample in a homogeneous form. The sample was then weighted for applying in the separation
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systems by NIELC.9
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2.2 Reagents
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Ion-exchange resins MP-1 (anionic) and PM-50 (cationic) were obtained from Biorad
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Laboratories (Richmond, CA, USA) with particle sizes of 200-400 mesh (37-75 µm). These resins
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were used for separation of acidic, basic and neutral sulfur compounds by non-aqueous ion
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exchange liquid chromatography (NIELC).9 Methanol, isooctane, benzene, cyclohexane, ethyl
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ether, propanol, toluene, n-pentane, sulfuric acid, dichloromethane, sodium hydroxide were
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obtained from Merck (Damrstadt, Germany). Propylamine was obtained from Sigma-Aldrich (St.
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Louis, MO, USA).
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2.3 Samples
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A total of 23 samples of asphaltic cements were analyzed in this work for asphaltenes and
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maltenes content. Five samples of asphalt cements were studied before and after the three aging
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processes (described below) and analyzed in a comparative way for speciation purposes. The
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samples were supplied by five different refineries in Brazil and analyzed as received.
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2.4 Analytical procedures
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2.4.1 Separation of asphaltenes and maltenes
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The separation of asphaltenic and maltenic fractions was carried out according to the
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ASTM D4124.20 Briefly, the sample was weighted and refluxed in isooctane (100 mL for each
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gram of sample). The mixture was heated and stirred once the reflux was initiated. The
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temperature was maintained at 99 °C by stirring for 1-2 h, until no observation of adherence of the
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asphalt matrix at the glassware. Once the asphalt cement was dissolved, the solution was stirred
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for 1 h longer. The solution was cooled and stirred for 2 h and the condensator was washed from
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top to bottom with 10-20 mL isooctane. After, this step, the solution was kept at resting for 2 h
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before filtration. The solution was filtered using vacuum and the residues of asphaltenes adhered
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to the glassware was washed with 100 mL isooctane by refluxing for 30 min. The filtration cake
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was washed with isooctane until it became colorless. The filtrate represents the soluble fraction
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(maltenes) and the residue of the funnel represents the insoluble fraction (asphaltenes). The
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obtained filtrate (maltenes) was evaporated in order to eliminate the solvent residue. Both the solid
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fractions (asphaltenes and maltenes) were weighted for calculating the mass balance of the
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process.
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2.4.2 Separation of acidic, basic and neutral compounds by NIELC
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The fractionation of asphalt matrix in acidic, basic and neutral compounds was carried out
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by using the NIELC method developed by Green et al.9 Briefly, 2.5 g of virgin asphalt cement was
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dissolved in ciclohexane and applied to a separation system containing two columns composed of
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a cationic and an anionic ion-exchange stationary phase connected in series. The columns were
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previously cleaned and activated according to the procedure. After applying the sample to the two
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column systems, ciclohexane (100 mL) was added and the neutral fraction was obtained. The
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columns were disconnected and treated separately. 10 mL of methanol was added to each
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disconnected columns and the aliquots were collected separately for using in the respective
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extraction procedure. The column containing the cation exchange resin was extracted in a Soxhlet
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system for 10 h with benzene and formic acid (10 mL) in order to obtain the acidic fraction. The
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column containing the anionic exchange resin was extracted in another Soxhlet system for 10 h
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with benzene and propylamine (10 mL) in order to obtain the basic fraction. After the extraction
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processes, the products were evaporated and weighted for determining the mass of the fraction.
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2.4.3 Aging process of asphaltic cements
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Three different procedures were used for simulating the aging process of asphalt cements.
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The Rolling Thin Film Oven Test (RTFOT) simulates the short term aging of asphalt during the
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hot mix, truck and silo storage, spray and compaction process, which takes place during its
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application. For this purpose, the assay is carried out at high temperatures and in the presence of
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oxygen (ASTM D 2872).21 The Pressure Aging Vessel (PAV) test was developed by the Strategic
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Highway Research Program (SHRP) and simulates the aging of the asphaltic binder in situ, i.e.,
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during its use as a road pavement at service temperatures. In the long term procedure, the asphalt
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sample is normally first conditioned using the RTFOT method. Thus, the residue from the RTFOT
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is placed in standard stainless steel pans and aged at the specified conditioning temperature for 20
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h in a vessel pressurized with air to 2.10 MPa. The conditioning temperature is selected according
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to the grade of asphalt cement. The residue is lastly vacuum degassed (ASTM D 6521).22 The
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SUNTEST aging procedure simulates a natural weathering of the asphalt cements under influence
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of UV radiation in pavement service.2 Herein, asphalt cements were also first conditioned using
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the RTFOT method and then submitted to UV radiation test (48 hours at 60ºC).
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2.4.4 Determination of total sulfur
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In order to approach the possible role of sulfur compounds present in acidic, basic and
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neutral asphalt fractions, the determination of total sulfur in the obtained fractions were carried out
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by combustion of the samples based on the determination of SO2 performed by infrared
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spectroscopy (ASTM D1552).23 All the samples of asphalt cements and its fractions were
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dissolved in toluene prior to the analysis.
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3. RESULTS AND DISCUSSION
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The chemical characterization of asphalt cements is a very important issue, since it is
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directly related to the physical performance of asphalts. However, the chemical speciation of
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sulfur compounds in maltenic and asphaltenic fractions and its relationship with the mechanisms
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that take place during the aging of asphalts has been little explored up to date. Thus, the
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distribution of sulfur compounds in different samples of asphalt cements produced by different
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Brazilian refineries was investigated. In a first step, 23 samples were characterized according to
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the distribution of asphaltenes and maltenes. In a second step, five samples were randomly
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selected for speciation studies of sulfur compounds and its relationship with the aging processes.
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The 23 samples investigated in this work showed a distribution of asphaltenes and
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maltenes with a significant higher amount of maltenes (90.6±5.0%) compared to asphaltenes
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(12.7±2.5%), as expected and previously reported for other asphaltic products.1,15,24,25 Thus, after
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characterizing the samples according to their asphaltenic and maltenic fractions, the speciation
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studies were conducted in order to elucidate the distribution of sulfur compounds within these
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fractions.
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3.1 Speciation of acidic, basic and neutral sulfur compounds in asphaltenes and maltenes
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According to Green,8−11 the fractionation of asphalt cements by ion exchange liquid
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chromatography
in
non-aqueous
medium
(NIELC)
is
based
on
the
obtaining
of
224
positively/negatively charged and neutral compounds using cationic and anionic exchange resins.
225
According to Payzant,12,13 the fractionation of dissolved asphalt cements in the ion exchange
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resins lead to the obtaining of acidic, basic and neutral fractions, which consist of the following
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majority sulfur compound classes: sulfoxides, sulfones, sulfides, thiophenes, mercaptans, and
228
sulfonic acids. Even being present in a variety of structures, the conditions during formation and
229
maturation of a petroleum reservoir can lead to the existence of some preferential forms. All these
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species can also be present as aliphatic or aromatic forms. Regardless the form they are present,
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sulfur compounds can be associated with three different oxidation states in asphalts: S(−2):
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sulfides, disulfides, thiols and thiophenes; S(+2): sulfoxides; and S(+4): sulfones and sulfonic
233
acids. Therefore, the chemical speciation of sulfur in asphalt cements can involve both their
234
oxidation states (redox speciation) and their binding forms (surrounding chemical environment).
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The sulfur charged structures separated in the ion exchange resins9 may be defined as the
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most reactive fraction, which is more susceptible to undergo oxidation, agglomeration, and
237
condensation reactions.15,24,25-28 As shown in Table 1, both the asphaltenic and maltenic fractions
238
in Brazilian asphalts are composed mostly of neutral compounds containing sulfur. After
239
fractionation of maltenes and asphaltenes into acidic, basic and neutral subfractions, we observed
240
a similar pattern in the total sulfur distribution. Despite the observed measurement deviations, the
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neutral fraction was found to be the majority fraction in maltenes and asphaltenes. This behavior
242
was observed for a total of 23 samples analyzed, considering merely the gravimetric determination
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of the solid products obtained after fractionating the acids, bases and neutral species.
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TABLE 1
246 247
The acidic, basic and neutral compounds containing sulfur present in asphalts allows us to
248
establish that: (1) most of the compounds present in asphalt cements (in both asphaltenes and
249
maltenes) are of neutral character (less reactive species); (2) acidic and basic compounds (more
250
reactive species) represent a minority fraction of asphalt cements. Furthermore, asphaltenes
251
presented the highest amount of polar compounds (25.3−50.9%) in the studied samples, herein
252
attributed to acidic and basic compounds that contain sulfur.
253
Considering a mechanistic approach based on the established sulfur organic chemistry, the
254
compounds of acidic and basic character found in asphaltenes and maltenes may have in their
255
structures the heteroatoms sulfur, nitrogen and oxygen. Possible structures of sulfur-containing
256
acidic compounds are associated mainly to aliphatic and aromatic positively charged species.
257
Besides sulfur, the presence of nitrogen in these structures may also contribute to the acidic
258
character of these compounds as a protonated group.29 Regarding the compounds of basic
259
character, possible structures may be associated mainly to aliphatic and aromatic negatively
260
charged species. Besides sulfur, the presence of nitrogen and oxygen in these structures should
261
also contribute to the basic character of the compounds. Thus, the basic character may be linked
262
directly to the sulfur heteroatom (e.g. sulfoxides, sulfonates, thiols and mercaptans) as well as the
263
concomitant presence of sulfur and nitrogen/oxygen heteroatoms in the structure of each
264
individual speciated compound.8,30−32
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By making a rationalization from the sulfur organic chemistry and previous work reporting
266
data from other asphalts,8, 30−32 one can postulate that sulfur and nitrogen containing compounds of
267
amphoteric character may also be present in both separated acidic and basic forms, depending on
268
the apparent pH of the media and pKa of each species. As hypothetical example, sulfur structures
269
such as sulfilimines and sulfoximines29 may be formed depending on the environmental
270
conditions. Likewise, compounds of acidic and basic character can be protonated or deprotonated
271
and, consequently, acquire the majority neutral form depending on the medium conditions. All
272
these possible acid-base equilibriums occurring in the medium of dissolved asphalt cement may
273
explain why sulfur functionalities defined as e.g. sulfides, thiophenes, and sulfoxides are almost
274
omnipresent in acidic, basic and neutral fractions.8 Additionally, acidic and basic funcionalities
275
such as carboxylic acids, phenols, indoles, carbazoles, amides, pyrroles, pyrimidines, pyridines,
276
quinolines, acridines, and phenazines may be present in these fractions30−32 separated by NIELC.
277
Moreover, the knowledge of the chemical speciation associated with sulfur and its surrounding
278
heteroatoms (N and O) is well recognized as the key to understanding the processes of conversion
279
and migration that take place during the aging of asphalts.9,10,26
280 281
3.2
Aging of asphalt cements and the speciation of sulfur compounds
282 283
The aging process of asphalt cements occurs mainly due to loss of mass by volatilization and
284
oxidation.1,9 These processes can significantly vary depending on the different sources of asphalt
285
cements. Other factors such as temperature, light effect, chemical reactions with aggregates may
286
also contribute to this process.1 According to some authors,8,24 asphalts should have a balanced
287
amount of polar and nonpolar molecules, which would lead to the homogeneity of the binder.
288
Furthermore, the balance of these compound classes plays a key role in the aging susceptibility
289
and performance of the asphalt binder, so that any chemical imbalance in this mixture may
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influence on its final quality.1
291
It is also well known that the aging of asphalts influences and alters the composition of
292
asphaltenes and maltenes in different ways.1,9,14,15,26 So an increased asphaltenic fraction and a
293
decreased maltenic fraction are expected after aging. Thus, the distribution of asphaltenic and
294
maltenic fractions in 5 virgin asphalt samples submitted to three aging processes (RTFOT,
295
RTFOT+PAV and RTFOT+SUNTEST) was investigated, which were lately studied for the
296
speciation involving sulfur compounds. As expected (figure 1), all the studied aging processes
297
lead to an increase in the asphaltenic fraction (figure 1A) in all the 5 samples of asphaltic cements.
298
These changes involve the formation of compounds high apparent molecular weight from
299
processes such as agglomeration and condensation.1,28 Furthermore, these new high apparent
300
molecular weight compounds may contain sulfur mainly in their higher oxidation states (+II and
301
+IV) forming sulfoxides and sulfones.9,33 For maltenes (figure 1B), it was observed that the
302
behavior was almost constant in the RTFOT aging, causing a small decrease in the RTFOT+PAV
303
aging and a more pronounced decrease in the RTFOT+SUNTEST process.
304 305
FIGURE 1
306 307
The subsequent separation of acidic (AF), basic (BF) and neutral (NF) fractions was
308
performed in maltenes and asphaltenes in order to identify the variations involving these classes
309
during the aging process. Taking into account that the RTFOT+SUNTEST process lead to the
310
more pronounced alteration in asphalt cements (figure 1), the 5 investigated samples were
311
analyzed in a comparative way for total sulfur distribution considering this process. It should be
312
also pointed out that the RTFOT+SUNTEST process takes into consideration also the effect of
313
sunlight in the asphalt aging, what is relevant for asphaltic cements used in pavements of tropical
314
countries. Figure 2 shows the behavior of sulfur compounds in virgin and RTFOT+SUNTEST
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aged samples in a comparative way for asphaltenes. As can be seen, the average percentage of
316
acidic, basic and neutral fractions showed an increase of acid (AF) and basic (BF) sulfur
317
compounds, while the neutral compounds (NF) decreased.
318 319
FIGURE 2
320 321
Furthermore, an overall increase of about 22% of the most reactive fractions (AF + BF) in
322
asphaltenes after aging is probably related to the oxidation, condensation and agglomeration
323
reaction of sulfur compounds, which may also partially migrate from maltenes. In contrast, the
324
neutral fraction (FN) decreased by about 23%. In the case of maltenes (figure 3), the behavior of
325
sulfur compounds after aging is similar to that shown for asphaltenes. As can be seen, the average
326
percentage of acidic, basic and neutral fractions for 5 samples showed an overall increase of ~32%
327
in the more reactive fractions, while the neutral fraction (NF) decreased ~30% after aging by the
328
RTFOT+SUNTEST process.
329 330
FIGURE 3
331 332
The loss of neutral compounds in both the asphaltenic and maltenic fractions may be also
333
associated with volatilization, agglomeration and condensation reactions forming sulfur, carbon
334
and nitrogen compounds of higher polarity.14,28 These reactions can lead also to the transformation
335
of aromatics into resins and the resins into asphaltenes, resulting in a continuing increase of heavy
336
fractions14,28 and the consequent hardening of the asphalt cement. However, the aging of asphalts
337
according to these well-known majority processes was not yet specifically explained in terms of
338
distribution of sulfur compounds of acid-base character in asphaltenes and maltenes. Furthermore,
339
the observed transformations of neutral aromatics into polar compounds (resins) may be related to
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ring-open reactions observed for thiophenic fractions within the studied samples. For supporting
341
this hypothesis, a dominant process was observed in this work involving thiophenes separated by
342
the method proposed by Payzant and co-workers.13 After performing these experiments in 5
343
different asphaltic cements, a decrease of thiophenic compounds in the range 24.3−48.2% after
344
aging by RTFOT+PAV process22 was observed.
345 346
3.3 Speciation of sulfur compounds and the aging susceptibility of asphalt cements
347 348
The aforementioned and discussed results for acidic, basic and neutral fractions of
349
maltenes and asphaltenes may also be approached in terms of chemical reactivity of the sample.
350
Herein, polar compounds may confer a higher reactivity to the asphalt involving their more active
351
sites (acidic and basic functionalities). Therefore, the sum of the most reactive fractions (AF + BF)
352
divided by the less reactive fraction (NF) is proposed as a calculation index for reactivity of the
353
asphaltic cements. Thus, the sample that presents the highest reactive fraction will be the one,
354
which is more susceptible to aging. This calculation can be expressed according to the equation:
355 356 357
Ir = AFa + BFa + AFm + BFm NFa + NFm
358 359
where Ir is the reactivity index, AFa and BFa the basic and acidic fractions of asphaltenes;
360
AFm and FBm are the acidic and basic fractions of maltenes; and NFm and NFa the neutral fractions
361
of asphaltenes and maltenes, respectively. This calculation considers the sum of the more reactive
362
fractions divided by the sum of the less reactive fractions of the whole asphalt (maltenes +
363
asphaltenes). Table 2 summarizes the results in terms of reactivity of the asphalt cement compared
364
to the content of total sulfur and asphaltenes for the 5 studied virgin and aged asphalt samples. The
365
reactivity index can be also calculated specifically to each fraction of asphaltenes and maltenes
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Page 16 of 28
366
containing AF, BF and NF. Herein, a similar distribution of the samples was achieved concerning
367
their reactivity and aging susceptibility.
368
As can be seen, a higher concentration of total sulfur in asphalts does not imply necessarily
369
in a higher reactivity (susceptibility to aging) of the cement. Therefore, the chemical speciation
370
regarding the classes of sulfur compounds in the asphalt structure play a more important role and
371
may count lastly for a higher or lower resistance of the asphalt to the aging. Herein, compounds of
372
acidic and basic character seem to be crucial for understanding these processes and for quantifying
373
the chemical stability of the asphalt cement according to chemical parameters as well. So these
374
results suggest a classification of asphalt cements in terms of their susceptibility to aging
375
(reactivity) based on the chemical speciation of sulfur compounds, which is normally based on
376
physical parameters. Furthermore, this knowledge would allow the production of more stable
377
binder mixtures.
378 379
The classification of the studied samples considering their susceptibility to aging based on the chemical reactivity (calculated as Ir) can be expressed as follows:
380 381 382
Asphalt cement samples:
A1 < A3 < A2 < A4 < A5 Reactivity
383 384
According to the reactivity classification regarding the total sulfur distribution and
385
asphaltenes in virgin asphalt samples, there is a high similarity between asphaltene composition
386
and reactivity based on sulfur compounds. So sample A1 presented a lower reactivity and lower
387
content of asphaltenes, whereas sample A5 is the one with higher reactivity and higher content of
388
asphaltenes (table 2). However, it can vary from sample to sample. This situation suggests that a
389
higher content of asphaltenes may be related, but not necessarily imply in a higher reactivity of the
390
asphalt cement, as can be observed for samples A4 and A5 (table 2). This would depend on the
391
sample, which has specific functional groups related to their heteroatoms (S, N and O),
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characterizing a greater or lesser susceptibility of the cement to aging. Furthermore, it was
393
observed that the less reactive sample (A1) presented the highest amount (>80%) of neutral sulfur
394
compounds in maltenic fraction of asphalt. Considering that this sample suffered the higher
395
variation of Ir after aging (table 2), one can infers that the most important chemical transformation
396
in the asphaltic cement occurred in maltenes involving all neutral compounds. Considering that
397
oxidative aging is also a time-dependent process, asphalt cements having neutral compounds as a
398
majority class seem to be more resistant to aging by RTFOT+SUNTEST process. Additionally,
399
the neutral fraction of maltenes has probably amphoteric compounds that may be involved in the
400
chemical transformations taking place during aging. Furthermore, sample A1 presented the higher
401
variation of asphaltene content (+3.0%) after aging (table 2). Since this sample presented the
402
lower asphaltene content (virgin sample), the higher variation of Ir after aging is related mostly to
403
the increasing of acidic and basic sulfur compounds in this fraction, which may partially migrate
404
from maltenes as oxidized compounds (e.g. sulfoxides and sulfones). As can be also observed in
405
table 2, sample A5 suffered less pronounced transformations in asphaltenic fraction (+0.1%), what
406
is probably related to a high initial concentration of polar compounds (Ir = 1.18) present as
407
asphaltenes in this cement. Beyond compounds containing sulfur, ketone formation has been also
408
identified as a major factor that lead to asphaltene formation, being asphaltenes the primary
409
responsible for viscosity increase on asphalt aging.34,35 In addition, it is already known that the
410
formation of ketone functional groups changes the polarity and solubility of the associated
411
condensed aromatic ring compounds, so that they can agglomerate and become part of the
412
asphaltene fraction.3
413 414 415 416
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417
4.
Page 18 of 28
CONCLUSIONS
418 419
Asphalt cement is a matrix of highly complex constitution, which depends also on their
420
origin. The results discussed in this work were important for deepening the knowledge about the
421
influence of sulfur chemical speciation on the asphalt quality. Thus, the RTFOT+SUNTEST
422
process was studied in a comparative way for 5 asphalt cements samples, since it was the process
423
that caused the more pronounced changes in maltenes and asphaltenes among 23 different samples
424
supplied by different refineries. It was found that the aging of asphalt cement leads to an increase
425
of the more reactive fractions of sulfur (acidic and basic) in both asphaltenes and maltenes. In
426
addition, a decrease in the less reactive fraction (neutral) was observed in both asphaltenes and
427
maltenes. This study also showed the importance of other heteroatoms, such as nitrogen and
428
oxygen, bound to sulfur (or surrounding it) in the asphalt chemical structure, what may influence
429
on the susceptibility of the asphalt cement to aging. It was observed that sulfur appears in larger
430
amounts in the less reactive fraction (neutral) in both maltenes and asphaltenes. Herein, a
431
classification of the studied samples was proposed taking into account the reactivity calculated in
432
terms of acidic, basic and neutral compounds. It was also observed that the less reactive sample
433
(A1) presented the highest amount (>80%) of neutral sulfur compounds in maltenic fraction of
434
asphalt. Therefore, the presence of functional groups related to their specific heteroatoms seemed
435
to be definitive to explain a greater or lesser susceptibility of asphalts to aging.
436
Lastly, this study contributed to a greater understanding on the aging processes in asphalt
437
cements regarding the speciation of sulfur compounds. This understanding is necessary to improve
438
the quality of the final product, allowing the production of cements that could be more resistant to
439
aging as well as the development of processes to retard it. Moreover, the establishment of specific
440
markers within the sulfur compounds (e.g. aryl/alkyl sulfidic or tiophenic acids and bases) that
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could define an asphalt binder of greater or lesser aging resistance might be studied from this
442
approach on.
443 444
ACKNOWLEDGEMENTS
445 446
The authors acknowledge the financial support provided by the foundations CNPq and
447
CAPES. The authors also greatly acknowledge the financial support from PETROBRAS through
448
the Center of Research and Development “Leopoldo Américo Miguez de Mello” (CENPES).
449 450 451
REFERENCES
452 453
(1)
Siddiqui, M. N; Ali, M. F. Studies on the aging behavior of the Arabian asphalts. Fuel 1999, 78, 1005−1015.
454 455
(2)
Whiteoak, D. SHELL Bitumen handbook. SHELL, England, 1990.
456
(3)
Petersen, J. C.; Glaser, R. Asphalt oxidation mechanisms and the role of oxidation products on age hardening revisited. Road Mat. Pav. Design 2011, 12, 795−819
457 458
(4)
asphalts. Anal. Chem. 1974, 46, 2242−2246.
459 460
(5)
Petersen, J. C. A dual, sequential mechanism for the oxidation of petroleum asphalts. Petrol. Sci. Technol. 1998, 16, 1023−1051.
461 462
Dorrence, S. M.; Barbour, F. A.; Petersen, J. C. Direct evidence for ketones in oxidized
(6)
Aleshin, G. N.; Altukhova, Z. P.; Antipenko, V. R.; Marchenko, S. P.; Kam’yanov, V. F.
463
Distribution of vanadium and vanadyl porphyrins in petroleum distillates of different
464
chemical types. Petrol. Chem. U.S.S.R. 1984, 24, 191-195.
ACS Paragon Plus Environment
19
Energy & Fuels
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
465
(7)
Page 20 of 28
Zhao, X.; Liu, Y.; Xu, C.; Yan, Y.; Zhang, Y.; Zhang, Q.; Zhao, S.; Chung , K.; Gray, M. R.;
466
Shi, Q. Separation and characterization of vanadyl porphyrins in Venezuela Orinoco heavy
467
crude oil. Energ. Fuels 2013, 27, 2874–2882.
468
(8)
Types in Asphalt. Energ. Fuel 1993, 7, 119−126.
469 470
Green, J. B.; Yu, S. K. T.; Pearson, C. D.; Reynolds, J. W. Analysis of Sulfur Compound
(9)
Green, J. B.; Hoff, J.; Woodward, P. W.; Stevens, L. L. Separation of liquid fossil fuels
471
into acid, base and neutral concentrates: 1. An improved nonaqueous ion exchange method.
472
Fuel 1984, 63,1290− −1301.
473
(10)
Green, J. A.; Green, J. B.; Grigsby, R. D.; Pearson, C. D.; Reynolds, J. W.; Shay, J. Y.;
474
Sturm Jr., G. P.; Thomson, J. S.; Vogh, J.W.; Vrana, R. P.; Yu, S. K-T.; Diehl, B. H.;
475
Grizzle, P. L.; Hirsch, D. E.; Hornung, K. W.; Tang, S-Y.; Carbognani, L.; Hazos, M.;
476
Sanchez, V. Analysis of Heavy Oils: Method Development and Application to Cerro Negro
477
Heavy Petroleum. Topical Report NIPER-452, NTIS No. DE90000201; NTIS: Springfield,
478
VA, 1989; Chapter 4.
479
(11)
Green, J. A.; Green, J. B.; Grigsby, R. D.; Pearson, C. D.; Reynolds, J. W.; Shay, J. Y.;
480
Sturm Jr., G. P.; Thomson, J. S.; Vogh, J. W.; Vrana, R. P.; Yu, S. K-T.; Diehl, B. H.;
481
Grizzle, P. L.; Hirsch, D. E.; Hornung, K. W.; Tang, S-Y.; Carbognani, L.; Hazos, M.;
482
Sanchez, V. Analysis of Heavy Oils: Method Development and Application to Cerro Negro
483
Heavy Petroleum. Topical Report NIPER-452, NTIS No. DE90000200; NTIS: Springfield,
484
VA, 1989; Chapter 3.
485
(12)
1986, 9, 357−369.
486 487
Payzant, J. D.; Montgomery, D. S.; Strausz O. P.. Sulfides in petroleum. Org. Geochem.
(13)
Payzant, J. D.; Mojelsky, T. W.; Strausz, O. P. Improved Methods for the Selective
488
Isolation of the Sulfide and Thiophenic Classes of Compounds from Petroleum. Energ.
489
Fuels 1989, 3, 449−454.
ACS Paragon Plus Environment
20
Page 21 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
490
Energy & Fuels
(14)
Mat. 2002, 16, 15−22.
491 492
Lu, X.; Isacsson, U. Effect of ageing on bitumen chemistry and reology. Constr. Build.
(15)
Qin, Q.; Schabron, J. F.; Boysen, R. B.; Farrar, M. J. Field aging effect on chemistry and
493
rheology of asphalt binders and rheological predictions for field aging. Fuel 2014, 121,
494
86−94.
495
(16)
of environmental aging on Colombian asphalts. Fuel 2014, 115, 321–328.
496 497
Fernández-Gómez, W. D.; Quintana, H. A. R.; Daza, C. E.; Lizcano, F. A. R. The effects
(17)
Lee, S. J.; Amirkhanian, S. N.; Shatanawi, K.; Kim, K. W. Short-term aging
498
characterization of asphalt binders using gel permeation chromatography and selected
499
Superpave binder tests. Constr. Build. Mater. 2008, 22, 2220−2227.
500
(18)
Introducing two new techniques. Fuel 2014, 118, 365–368.
501 502
Fischer, H. R.; Dillingh, E. C. On the investigation of the bulk microstructure of bitumen –
(19)
Rebelo, L. M.; de Sousa, J. S.; Abreu, A. S.; Baroni, M. P. M. A.; Alencar, A. E. V.;
503
Soares, S.A.; Mendes Filho, J.; Soares, J. B. Aging of asphaltic binders investigated with
504
atomic force microscopy. Fuel 2014, 117, 15–25.
505
(20)
ASTM D4124-09. Standard Test Method for Separation of Asphalt into Four Fractions.
506
(21)
ASTM D2872. Standard Test Method for Effect of Heat and Air on a Moving Film of Asphalt (Rolling Thin Film Oven Test).
507 508
(22)
Pressurized AgingVessel (PAV).
509 510
(23)
ASTM D1552. Standard Test Method for Sulfur in Petroleum Products (High-Temperature Method).
511 512
ASTM D6521-08. Standard Pratice for Accelerated Aging of Asphalt Binder Using a
(24)
Zhang, F.; Yu, J.; Han, J. Effects of thermal oxidative aging on dynamic viscosity,
513
TG/DTG, DTA and FTIR of SBS- and SBS/sulfur-modified asphalts. Constr. Build. Mater.
514
2011, 25,129−137.
ACS Paragon Plus Environment
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Energy & Fuels
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
515
(25)
Mastrofini, D.; Scarsella, M. The application of rheology to the evaluation of bitumen ageing. Fuel 2000, 79, 1005-1015.
516 517
Page 22 of 28
(26)
Michalica, P.; Daucik, P.; Zanzotto, L. Monitoring of compositional changes occurring
518
during the oxidative aging of two selected asphalts from different sources. Petroleum &
519
Coal 2008, 50, 1−10.
520
(27)
asphaltenes from heavy petroleum feedstocks. Fuel 1984, 63, 141−146.
521 522
Spheight, J. G.; Long, R. B.; Trowbridge, T. D. Factors influencing the separation of
(28)
Sugano, M.; Kajita, J.; Ochiai, M.; Takagi, N.; Iwai, S.; Hirano, K. Mechanisms for
523
chemical reactivity of two kinds of polymer modified asphalts during thermal degradation.
524
Chem. Eng. J. 2011, 176-177, 231−36.
525
(29)
York, 1977, p. 232−602.
526 527
(30)
Dutta, P. K.; Holland, R. J. Acid-base characteristics of petroleum asphaltenes as studied by non-aqueous potentiometric titrations. Fuel 1984, 63, 197−201.
528 529
Oae, S. Organic Chemistry of Sulfur. University of Tsukuba, Japan. Plenum Press, New
(31)
Okuno, I.; Latham, D. R.; Haines, W. E. Type Analysis of Nitrogen in Petroleum Using
530
Nonaqueous Potentiometric Titration and Lithium Aluminum Hydride Reduction. Anal.
531
Chem. 1965, 37, 54−57.
532
(32)
asphaltite and oil shale pyrolysis products. J. Anal. Appl. Pyrol. 1990, 17, 227−235.
533 534
Önen, A.; Sarac, A. S. Nonaqueous potentiometry for analyses of nitrogen bases from
(33)
Waldo, G. S.; Mullins, O. C.; Penner-Hahn, J. E.; Cramer, S. P.; Determination of the
535
chemical environment of sulphur in petroleum asphaltenes by X-ray absorption
536
spectroscopy. Fuel 1992, 71, 53−57.
537
(34) Petersen, J. C. A review of the fundamentals of asphalt oxidation – chemical,
538
physicochemical,
physical
property
and
durability
539
Transportation Research Board, Washington, DC, October 2009.
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No.
E-C140,
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540
Energy & Fuels
(35)
Lin, M. S.; Linsford, K. M.; Glover, C. J.; Davidson, R. R.; Bullin, J. A. The effects of
541
asphaltenes on the chemical and physical characteristics of asphalts, Asphaltenes:
542
Fundamentals and Applications, E.Y. Shen and O.C. Mullins, eds., Plenum Press, N.Y.,
543
1995, p. 155-176.
544 545 546
Captions to the figures
547 548
Figure 1 – Distribution pattern (n = 3) of asphaltenes (A) and maltenes (B) in asphalts submitted
549
to the aging processes RTFOT, RTFOT+PAV and RTFOT+SUNTEST compared to a virgin
550
cement sample.
551 552
Figure 2 – Distribution pattern (n = 3) of sulfur in acidic, basic and neutral compounds in
553
asphaltenes of virgin and aged asphalts (N = 5). AF: Acidic fraction; BF: Basic fraction; NF:
554
Neutral fraction. All the results are expressed as the average values related to 5 different asphalt
555
cements (described in section 2.3).
556 557
Figure 3 – Distribution pattern (n = 3) of sulfur in acidic, basic and neutral compounds in
558
maltenes of virgin and aged asphalts (N = 5). AF: Acidic fraction; BF: Basic fraction; NF: Neutral
559
fraction. All the results are expressed as the average values related to 5 different asphalt cements
560
(described in section 2.3).
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Table 1. Total sulfur distribution regarding acidic, basic and neutral compounds in asphalt fractions (maltenes and asphaltenes) Sulfur distribution (%) a
Sample Acidic compounds b
Basic compounds c
Neutral compounds d
Asphaltenes
Maltenes
Asphaltenes
Maltenes
Asphaltenes
Maltenes
A1
14.6
6.6
22.1
5.1
63.3
88.3
A2
10.8
24.1
14.5
22.4
74.7
53.5
A3
12.3
13.9
15.8
24.6
71.9
61.5
A4
23.5
15.7
24.1
20.5
52.4
63.8
A5
17.9
26.6
33.0
30.4
49.1
43.0
562
a
Mean values (n=3); b RSD (Relative standard deviation; n=3): 21.8−28.3%; c RSD (Relative standard deviation; n=3): 25.0−31.0%;
563
d
RSD (Relative standard deviation; n=3): 18.9−30.8%
564
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Table 2. Characterization of virgin and aged asphaltic cements regarding the content of total sulfur, reactivity index (Ir) and asphaltenes.
566
Sample
Total S (%) a
567
Ir
Asphaltene content (%)
Virgin asphalt
Aged asphalt b
Virgin asphalt
Aged asphalt b
568
A1
2.2
0.32
2.23
8.6
11.6
569
A2
3.4
0.56
2.09
10.2
12.7
570
A3
3.1
0.50
1.46
11.0
13.8
571
A4
1.8
0.72
1.27
14.5
15.0
572
A5
3.1
1.18
1.72
13.4
13.5
573
a
RSD (Relative standard deviation; n=3): 8.0−15.0%
574
b
Asphalt cements aged by RTFOT+SUNTEST methods
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575 576 577
Figure 1
578
579 580
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581 582 583
Figure 2
584
585 586 587
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588 589 590 591
Figure 3
592
593
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