Silver is a soft white transition metal with 47 atomic number which is represented by Ag symbol. Ag has the most thermal and electrical conductivity among other metals and its most common oxidation state is Ag (I). This metal is widely utilized in the production of coins, mirrors, electrical devices, pharmaceutical products, cosmetics, jewelry, batteries, catalysts and photographic films [1-3]. Therefore, its discharge in the environment and getting exposure to living organisms is highly probable. And due to the fact that Ag can cause severe and irreversible damages including nausea, diarrhea, shock, respiratory irritation, liver and kidney malfunctions, skin irritation, cardiovascular disease and different types of cancer for humans, its determination and removal from environmental specimens is extremely significant. The next matter that accentuates the importance of silver removal is the price of this metal [4-6]. Because recycling of Ag can reduce the expenses of the aforementioned industries and increase their increment. In this regards, many studies have been focused on the determination and removal of this toxic and precious metal .
Despite the fact that numerous analytical methods such as atomic absorption spectroscopy with both flame and graphite furnace atomizers, inductively coupled atomic emission spectroscopy (ICP-AES) and UV-Visible spectrophotometry have been designed for determination of Ag+, but most of them have conspicuous disadvantages that make them undesirable [8-10]. For instance, intricate instrumentation, being expensive and time-consuming analysis procedures are the most problems of the referred methods. Fortunately, as an ideal alternative for the cited analytical techniques, we can refer to electrochemical and thermal sensors because these types of sensors are economical, time-saving, portable, selective, sensitive and straightforward. But the main step in the construction of a sensor is finding an appropriate sensing material [11-13].
In addition, a lot of approaches like electrolysis, precipitation, ion flotation, ion exchange, and membrane separation have been developed for removal of Ag+ ions. However, these techniques are not thrifty because they are based on the instruments that are extremely expensive [14-16]. Owing to the fact that reducing the expenses of pollutants’ removal procedures can play a decisive role in encouraging various industries to paying more attention to environmental issues. Allocating more researches to low-cost methods such as adsorption seems logical [17-20].
On the other hand, graphene which its structure is given in Fig. 1, is a hexagonal lattice of carbon atoms. In this two-dimensional nano-structure, sp2 hybridized carbon atoms are bonded to each other [21-24]. Owing to the fact that, graphene is a porous carbon substance which has an outstanding specific surface area and unique structure, it has excellent physical and chemical properties for adsorption and removing various compounds and it is one of the most widely used adsorbents for eliminating environmental pollutants [25-27]. Moreover, its specific electrical features make it an ideal electroactive sensing material for electrochemical detection of various analytes. In this regard, it was decided to evaluate the interaction of silver (I) with graphene and the impact of doping graphene with silicon and germanium on this process by density functional theory for the first time.
In this study, the structures of Ag+, graphene, and Ag-graphene complex were designed primarily by using Gauss View 3.1 and nanotube modeler 188.8.131.52 software. Then, geometrical optimizations, IR and frontier molecular orbital calculations were performed on them via Spartan software. All of the calculations were implemented in the aqueous phase and in the temperature range of 298.15 - 398.15 K at 10º intervals. In order to evaluate the effect of doping graphene with silicon and germanium on the adsorption of silver (I), the central ring of each graphene sheet was doped with silicon, germanium and also both of them (co-doping) in three ortho, meta and para situations. Afterward, the cation was inserted in the same place near the central ring for implementing the mentioned computations. It should be noted that silicon and germanium were chosen as dopant atoms because both of them are in the carbon group at the periodic table and they have similar valence and properties to carbon. The next matter that supports selecting these elements as dopant atoms is that in previous researches, doping graphene with silicon and germanium had led to noteworthy and meaningful results. All calculations were carried out at B3LYP/6-31G(d) level of density functional theory. This basis set was selected because it had produced results which were in good accordance with experimental data in our former researches [27-37]. The studied reaction was as follows:
Ag+ + adsorbent→ Ag+ -adsorbent
RESULTS AND DISCUSSION
Owing to the fact that adsorption of Ag+ on the surface of pure and doped graphene was evaluated in ten different situations. For better and more convenient understanding, each condition is called by an abbreviated name. Therefore, explaining the naming method and abbreviations is essential. In this regards, the naming method is described at the following:
At the first step, the capability of the pure graphene which was consisted of only carbon atoms in the adsorption of the studied contaminant was investigated. The pure graphene is shown as PG in this paper and its derivative with silver is demonstrated by Ag-PG abbreviation.
Then the graphene was doped with silicon at three ortho, meta and para circumstances. As it can be seen in Figs. 2 and 3, the dopant elements are numbered with one and two consecutively in order to report the bond lengths more easily. The ortho silicon doped graphene is symbolized by OSDG and its derivative with silver is defined as Ag-OSDG. The meta silicon doped graphene is remarked by MSDG abbreviation and Ag-MSDG is specified for its derived product with silver. The PSDG and Ag-PSDG signs were assigned for para silicon doped graphene and its complex with Ag+ respectively.
In the third step, the graphene was doped with germanium at three ortho, meta and para positions. The OGDG and Ag-OGDG were heeded as symbols for ortho germanium doped graphene and Ag-ortho germanium doped graphene respectively. The meta germanium doped graphene was abbreviated as MGDG and its derived complex with Ag+ is exhibited by Ag-MGDG sign. The PGDG and Ag-PGDG symbols were also considered for para germanium doped graphene and Ag-para germanium doped graphene.
In the end, the nano-adsorbent was doped with one silicon and one germanium elements in ortho, meta and para situations. The ortho co-doped graphene and its silver derivative were remarked as OCDG and Ag-OCDG respectively. MCDG and Ag-MCDG stand for meta co-doped graphene and its silver derived product. PCDG was allocated for para co-doped graphene and Ag-PCDG was determined for the derived product of silver and para co-doped graphene interaction.
Adsorption Energy Values
In order to achieve adsorption energies of silver (I) on the surface of the 10 nano adsorbents, geometrical optimizations were implemented on the structures of Ag+, ordinary and doped graphenes and their derivatives. Then adsorption energy values were calculated by the succeeding equation:
Eads= E Ag-adsorbent – (E Ag + E adsorbent) (1)
Afterward, the obtained results were reported in Table 1. As the provided data in the table reveals clearly the adsorption energy of the pure graphene (-477.03 KJ/mol) is more positive than the other doped graphenes. Indeed, by superseding two carbon atoms with silicon and germanium, the adsorption process has become more experimentally feasible. In the case of silicon doped graphenes, Ag-OSDG has the lowest adsorption energy (-814.911 KJ/mol) but by increasing the distance of the dopant atoms, this parameter has become more positive gradually so that PSDG has the most positive adsorption energy among the silicon-doped graphenes (-669.450 KJ/mol). On the other hand, in the case of germanium doped nano-adsorbents, there is not seen any regular trend. We cannot find an obvious relationship between the adsorption energy and the distance of the germanium atoms. Because Eads has decreased from -774.667 KJ/mol in the ortho situation to the -901.534 KJ/mol in the meta position. But by enhancing the distance of the germanium atoms in the para condition this variable has risen significantly to -605.590 KJ/mol. Nevertheless, it seems ortho co-doped graphene which is entailed of one silicon and one germanium elements has the best interaction with silver owing to its lowest adsorption energy (-1143.038 KJ/mol). The next matter that can be perceived from the table is that co-doped graphenes exhibit a similar trend towards Ag+, to Si-doped graphenes. In other words, by incrementing the distance between the dopant atoms, Eads experience a dramatic surge from the -1143.038 KJ/mol in ortho position to -560.783 KJ/mol at para condition .
It is worth mentioning that according to the carried out calculations there was not observed any negative frequency in all of the investigated structures. The lowest frequency for all of the derivatives is also reported in Table 1.
Calculation and Verifying the Values of Enthalpy Changes (∆Had)
In order to obtain enthalpy alterations, the thermal enthalpy values for the reactants and products of the adsorption process that had been computed by the software were inserted in the following formula:
ΔHad = ΔEº + (Hth (Ag-adsorbent) – (Hth (sliver) + Hth (adsorbent))) (2)
In the aforementioned equation, ΔEº stands for the variations in the total energy of the desired procedure. As the provided data in Table 2, demonstrates obviously, ΔHad has fallen significantly after doping graphene with two other elements. In fact, adsorption of Ag+ on the surface of the doped nano-adsorbents is more exothermic than its adsorption on the pure graphene. Among Si-doped graphenes, OSDG has the lowest ΔHad value (-812.085 KJ/mol in the room temperature) but by increasing the distance of the dopant elements in meta and para positions, this parameter has got more positive. This pattern is also observed in co-doped graphenes. As it can be witnessed from the table, Ag-OCDG has the most negative (-1131.077 KJ/mol) among all of the studied derivatives. It means silver can be absorbed by the ortho co-doped graphene more exothermically than the other ones. However, the enthalpy changes values of Ag-MCDG and Ag-PCDG is substantially more positive than Ag-OCDG. In the case of germanium doped graphenes, the ΔHad does not show any dependence to the situations and closeness of the germanium atoms because enthalpy alterations value has decreased from -774.001 KJ/mol Ag-OGDG to -889.653 KJ/mol. On the other hand, this variable has reduced again to -608.565 KJ/mol in Ag-PGDG derivative.
For evaluating the impression of temperature on the adsorption process of the silver ions the IR calculations were implemented in the temperature range of 298.15-398.25 K at 10-degree intervals. As it is apparent from the table in all derivatives ΔHad experiences a modest and negligible rise by gradual enhancing the temperature. So generally, temperature variations do not have a tangible impact on the enthalpy changes.
Calculation and Verifying the Values of Gibbs Free Energy Changes (∆Gad) and Thermodynamic Constant (Kth)
For calculating Gibbs free energy changes for the adsorption process the subsequent equation would be utilized:
ΔGad = ΔEº + [Gth (Ag-adsorbent)]-[ Gth (Silver) + Gth (Adsorbent)] (3)
In this formula, Gth is thermal Gibbs free energy for the reactants and the products of the interaction between the heavy metal and nano-adsorbents and ΔEº is the alterations in the total energy of the system. As the reported ΔGad values in Table 3 exhibit obviously, the Gibbs free energy alterations for the adsorption of Ag+ on the ordinary graphene is more positive than the doped graphenes which imply that silver can be absorbed by the doped graphenes more spontaneously. The achieved ΔGad values are in good agreement with the previously obtained adsorption energies and enthalpy changes. Ag-OCDG has the most negative Gibbs free energy alteration values with a great discrepancy. In silicon doped graphenes Ag-OSDG has lower ΔGad than Ag-MSDG and Ag-OGDG. In the case of germanium doped graphenes, the most negative ΔGad is seen at meta position (-847.404 KJ/mol at ambient temperature) and this parameter is more positive for para and ortho situations due to their higher ΔGad. It seems the increasing of the temperature cause a slight decline in the Gibbs free energy values. Indeed, the temperature variations do not cause a remarkable change in this variable [28-30].
The thermodynamic equilibrium constants were also calculated for the desired adsorption process by using equation 4 and the achieved results were tabulated in Table 4. As it can be observed, the results are not out of expecting and ortho co-doped graphene shows the greatest thermodynamic equilibrium constant which is another proof that substantiates OCDG is the best adsorbent for silver cations. But the hidden point is that Kth has reduced tangibly by enhancing temperature. This phenomenon implies that the optimum temperature for the adsorption process is 298.15 K. Despite the fact that we observed a decline in the ∆Gad values for all derivatives by incrementing the temperature in the prior table but those alterations were not meaningful. In addition, owing to the fact that the temperature which is located in the denominator of equation 4 has changed more severely in comparison to ∆Gad, it shows its influence more sharply. Therefore, the thermodynamic equilibrium constant has decreased at higher temperatures. Hence, it can be deduced that 298.15 is the best temperature for the investigated procedure.
K = exp (- ΔGad / RT) (4)
Calculation and Inquiring the Specific Heat Capacity (CV)
The Specific heat capacity values of the silver, adsorbents and the derived product from the interaction between the heavy metal and pure and doped graphenes were computed by Spartan software and the obtained values were presented in Table 5. As it can be witnessed from the table, there is a considerable gap between the CV of the cation and evaluated nano-adsorbents, and after the adsorption of Ag+, a remarkable increase has taken place in the specific heat capacity of the investigated nanostructures. For example, in the case of pure graphene, the CV of Ag+ in the ambient temperature is 12.472 J/mol. K and the specific heat capacity for graphene are 303.479 J/mol.K but after the junction of silver on the surface of the graphene, this factor has risen to the value of 325.119 J/mol.K. This phenomenon can be seen in all of the situations. Due to the fact that CV has a linear and direct relationship with the thermal conductivity according to equation 5. Hence, it can be inferred the thermal conductivity of the ordinary and doped graphenes could be ameliorated after binding to silver ions. This phenomenon is worthwhile because, in the construction and development of thermal sensors, a meaningful variation in thermal conductivity is of great importance. Moreover, our prior studies in the ΔHad values proved that the adsorption procedure of Ag+ on all of the studied structures is exothermic and in other words, heat and energy are produced in this process and transferred from the system to the environment. Thus, production of heat and also defusing of specific heat capacity and thermal conductivity are valuable evidence which reveals that pure and doped graphenes can be eminent sensing materials for designing a silver (I) thermal sensor .
In the fifth equation, K, n, ˂ v ˃, λ, Cv and N are thermal conductivity, particles per unit, mean particle speed, mean free path, molecular specific heat capacity, and Avogadro’s number respectively. Fig. 4 depicts the influence of changing the temperature on the heat capacity of the ordinary and doped graphenes. As it is obvious from the diagram, by incrementing the temperature this parameter has also increased linearly. But with a closer look, it can be perceived that there is not a remarkable discrepancy between the pure graphene and the doped ones. In fact, all curves have a similar slope to each other and the only difference that can be witnessed among them is the negligible alterations in the intercept.
Frontier Molecular Orbital Analysis
Some Structural features including energies of HOMO and LUMO molecular orbitals (EH, EL), distance between energies of HOMO and LUMO molecular orbitals (HLG), electrophilicity (ω), dipole moment, maximum transmitted electron (ΔNmax) and chemical hardness (η) were also evaluated. HOMO and LUMO are the highest occupied molecular orbital and the lowest unoccupied molecular orbital respectively. And the energy difference between them is known as the HOMO–LUMO gap or energy gap (HLG) which could be calculated from equation 6. As it can be observed from the calculated energy gap values in Table 6 and also density of states (DOS) plots in Figs. 5 and 6, this parameter has increased after the adsorption of silver on the surface of all of the nano-adsorbents except in the case of pure graphene, PGDG, and MCDG. And owing to the fact a higher energy gap value of a compound exhibits that more excitation energy is required for conveying the electron to the excited state. Hence, it can be elicited that the conductivity of Ag+ and adsorbents has declined after the junction of the heavy metal in most cases except pure graphene, PGDG, and MCDG. The next matter that can be realized from the HLG values is that this variable is about 6-7.5 (eV) in all cases and has not experienced a significant alteration at all. In fact, all of the investigated structures are non-conductor and because the electrochemical conductometric analytical methods are designed on the basis of substantial variations in the electrochemical conductance of a system or reaction. Therefore, ordinary and doped graphene cannot be an appropriate material in the development of conductometric sensors for determination of Ag+.
Chemical hardness is the next investigated parameter which was calculated via equation 7. Chemical hardness is an excellent variable for estimating the softness of material. Indeed, a substance with a large HOMO-LUMO gap is harder than a compound with a small HOMO-LUMO gap. By a closer look at Table 6, it can be understood that graphene’s chemical hardness has reduced after doping it with silicon and germanium. Due to the fact that soft compounds can change their electron density more easily than hard materials. Hence, doped graphenes are more reactive than ordinary graphene. Because transmission of electrons which is necessary for the implementation of chemical reactions can be done more conveniently in the doped graphenes. After the attachment of silver ion on adsorbents, chemical hardness has incremented in all situations except pure graphene, PGDG, and MCDG.
Electrophilicity index (ω) is an admissible criterion for estimating the tendency of a molecule towards electron. This index was calculated via equation 8. While two molecules take part in a reaction, one of them behaves like a nucleophile, whereas the other one plays the role of an electrophile. A great electrophilicity value for a substance substantiates that the molecule has high electrophilic power. Thus, the quantity of ω describes the propensity of the system to acquire an additional electronic charge from the environment. The maximum amount of electronic charge index (∆Nmax) which was obtained by using equation 9, reveals the charge capacity of a system. In other words, a compound with a positive value of ∆Nmax index acts as an electron acceptor, whilst a molecule with a negative value of ∆Nmax index acts as an electron donor. As it can be seen from the provided data in the table, the cation has the most positive electrophilicity index and ∆Nmax (6.221 and 2.021 (eV) respectively) among all of the studied structures which shows that this cation behaves like a strong Lewis acid. But on the other hand, these parameters are lower for all of the nano-adsorbents with a tangible difference. therefore, it can be estimated that they can act the role of Lewis base or a ligand. By comparing the pure graphene and the doped ones it can be perceived that doping graphene with germanium and silicon leads to remarkable abate in both ω and ∆Nmax parameters. In fact, the affinity of the graphene to electron has decreased after the doping process. In other words, the doped graphenes can be a stronger Lewis base or ligand than the ordinary graphene. Hence, the toxic cation and doped graphenes with silicon and germanium can undergo the complexation reaction and this fact implies that doped graphenes could act as a prominent neutral ion carrier in the construction of potentiometric ion-selective electrodes for determination of Ag+. Another valuable point that is obvious from the table is that both of the ω and ∆Nmax variables have incremented after the junction of the silver ion on the surface of the adsorbents in all cases. So, the adsorbent has become more electrophile after the adsorption procedure .
HLG=ELUMO - EHOMO (6)
η = (ELUMO - EHOMO)/2 (7)
ω = µ2/2η (8)
∆Nmax=- µ/ η (9)
The dipole moment is a good standard for inspecting the solubility of a compound because it has a direct relationship with solubility. Indeed, structures with higher dipole moment values have better solubility in polar solvents like water. The achieved results from the calculation in the table show that the dipole moment has enhanced after the binding of silver to the adsorbents. Therefore, the solubility and reactivity of the system have improved after the junction. It is worth mentioning that in both removals of heavy metals and also sensor subjects, the low solubility of the adsorbent is of great importance. In this regards, it seems pure graphene, OSDG, OGDG, and OCDG structures are superior to other adsorbents in terms of low solubility owing to their negligible dipole moment values.
Silver is a toxic heavy metal that is widely utilized in various industries. Hence, it can be a potential contaminant for the environment. In addition, high dosages of Ag+ can cause severe and irreversible damages for all of the living organisms. Therefore, its removal and determination are very important. In this regard, the adsorption of Silver (I) cations on the surface of graphene and the influence of doping graphene with silicon and germanium on this process were investigated in this study at ten configurations. The achieved results show that ortho co-doped graphene has the best and the strongest interaction with Ag+ because it has the lowest adsorption energy, enthalpy changes, and Gibbs free energy alterations values among all of the evaluated adsorbents. The impact of temperature on the adsorption procedure was also studied and the obtained results reveal that the ambient temperature is the best and optimum temperature for all of the studied configurations. The calculated specific heat capacity values for all of the situations demonstrate that the thermal conductivity of all of the adsorbents has increased dramatically after the junction of the cation on the surface of the pure and doped graphenes. So, graphene could be a superb sensing material for construction of thermal sensors. Owing to the fact that energy gap values of all of the studied structures were considerably high, it seems ordinary and doped graphenes cannot be an appropriate electroactive sensing material in the development of conductometric sensors. But the obtained electrophilicity values exhibit that silver and all of the adsorbents can undergo complexation reaction. Thus, using pure and doped graphenes in the development of potentiometric ion-selective electrodes seems logical. Owing to the fact that the achieved results in this research prove the ortho silicon doped graphene has a strong interaction with Ag+, the capability of this nanostructure in the removal and determination of Silver (I) cations had better be investigated experimentally by the experts of this field.
CONFLICT OF INTEREST
The authors declare that there are no conflicts of interest regarding the publication of this manuscript.