Abstract
Hydrogels were synthesized by free radical graft copolymerization of itaconic acid (IA) onto corn starch (S-g-IA). For this purpose, potassium permanganate (KMnO4)-sodium bisulfite (NaHSO3) was used as redox initiation system. The formation of grafted starches was confirmed by Fourier transform infrared spectroscopy, wide angle X-ray scattering, thermogravimetric analysis and scanning electron microscopy. The effect of monomer concentration, neutralization, addition of crosslinking agent, N,N-bismetilenacrilamide (MBAm), and initiator concentration on grafting efficiency and adsorption capacity of the starch hydrogels was investigated. It was demonstrated that the introduction of carboxyl and carbonyl groups promoted starch hydration and swelling. Grafting degree increased with the decrease of monomer concentration, increase of initiator concentration, grade of neutralization and the addition of MBAm without neutralization. Remarkably the resulting materials exhibited water absorption capacities between 258 and 1878% and the ability to adsorb metal ions. It was experimentally confirmed the metal uptake, obtaining the higher adsorption capacity (q e = 35 mg/g) for the product prepared with the pre-oxidation and lower initiator concentration. The removal capacity order was Pb2+>Ni2+>Zn2+>Cd2+. Moreover, the experimental kinetic and the equilibrium adsorption data for Ni2+ and Pb2+ were best fitted to the pseudo-second order and Freundlich isotherm models, respectively. This work describes for the first time the preparation of metal removal hydrogels based on starch and itaconic acid using the pair redox system KMnO4/NaHSO3, which avoids the starch hydrolysis and allows itaconic acid grafting incorporation without the requirement of more reactive comonomers.
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Introduction
Heavy metals, due to their high toxicity, present a serious threat to flora and fauna. These metals, coming from industry or urban wastewater, produce the degradation of environment; [1] therefore, their removal is mandatory. The common treatments to remove metal ions from contaminated waters are mostly based on chemical precipitation, ion-exchange, adsorption, membrane filtration, coagulation–flocculation, flotation and electrochemical methods [2]. Most of these techniques require elevated energy; e.g. electroflotation methods. Precipitation and electrochemical processes present also several disadvantages, which include incomplete metal removal (amounts in the range 1–100 mg/L) and great sludge generation [3]. Membrane filtrations, ion-exchange among other are expensive. In this sense, the search for new products from natural resources, mainly polysaccharides, for metal remediation is not only indispensable but also beneficial [4–7]. These products can be biodegradable, cost-effective and nontoxic and can be used for agrochemicals release without risk of contamination or soil deterioration [4, 8, 9]. However, they can be low resistant to scratch, exhibit poor solubility, low mechanical properties, and instability at high temperatures and pHs during processing and with high tendency to retrogradation, expelling the water from the network. Nevertheless, these inconvenient can be overcome by chemical modification of the native polysaccharides.
It is well-known that one of the most abundant naturally occurring biopolymers is starch. It has diverse applications in areas of food, pharmaceuticals, textile, paper, and biomedical devices [10–14]. However, native starch can only show their water retention capacity but not efficient removal capacity for heavy metal ions [15]. One of the explored ways to improve this material is by radical copolymerization with vinyl monomers, such as acrylic acid, acrylamide among others [16–26]. Itaconic acid, another natural compound obtained from algae fermentation, has been widely used to modify natural products such as chitosan, alginate, cellulose, sisal [27–30] as well as starch [31–34]. To the best of our knowledge only one reported article dealing with the grafting copolymerization of itaconic acid with acrylamide as comonomer onto cassava starch using a redox system of ammonium persulfate (APS) and N,N,N′,N′-tetramethylethylenediamine (TEMED) to give pH responsiveness to the final superabsorbent hydrogel has been described [31]. The same group used in a previous work simultaneous irradiation technique for grafting polymerization of acrylic acid and acrylamide using gamma-rays as the initiator source [35]. None of these works use mild redox system avoiding the possibility of starch hydrolysis and therefore, the disablement of material. Besides they do not describe the grafting of itaconic acid using only this monomer.
Hebeish et al. [36] described the oxidation of starch using KMnO4 in presence of different reductants such as citric acid, oxalic acid and sodium sulphite, under various conditions of pH, temperature, time, and permanganate concentration. Later, they reveals [37] that potassium permanganate acts as initiator for polymerization of acrylonitrile monomer (AN) and as oxidizing agent for starch on the graft copolymerization of AN onto starch. Zhang et al. [16, 38, 39] also reported the use of potassium permanganate with citric acid, sulfuric acid, as initiator systems of graft copolymerization. They reported that Mn+7 is applied to the graft copolymerization, it directly oxidizes the hydroxyl groups on the polysaccharide backbone to form radicals, which can initiate the monomer to graft onto the backbone. The main drawback of this reaction is that some radicals on the backbone can have chain-transfer reactions onto the monomer, which can lead to the formation of the homopolymer. In this case, these two reactions, homopolymerization and copolymerization, are competitive, being more probable the graft copolymerization; while if peroxides are used as initiators, both reactions are taking place simultaneously.
Having in mind all the mentioned above, this article describes the starch modification by grafting polymerization of itaconic acid using KMnO4/NaHSO3 as initiator system to create a superabsorbent hydrogel able to efficiently remove heavy metals. Experimental parameters such as monomer content, neutralization degree, crosslinking agent, and initiator concentration were varied to obtain hydrogels for effective heavy metal removal. These hydrogels were structural and thermally characterized by FTIR, WAXS and TGA. Swelling behavior was also analyzed as a function of pH. Heavy metals removals for the different itaconic acid grafted starches were investigated individually or in combination with the other metals to analyze their selectivity. In addition, the equilibrium adsorption and the experimental kinetic data for selected systems were studied using Freundlich isotherm and pseudo-second order models, respectively.
Experimental
Materials
Native corn starch (NS) used was food grade obtained from Alfonso Rivas & Cía. Itaconic acid (C3H4(COOH)2, ≥99.9%, Merck) and N,N-methylene bis(acrylamide) (MBAm, 99%, Sigma-Aldrich) were used without purification. Hydrochloric acid (HCl, 37%), nitric acid (HNO3, 65%), sodium chloride (NaCl, 99%), silver nitrate (AgNO3, >99.9%), lead (II) nitrate (Pb(NO3)2, 99%), potassium permanganate (KMnO4, 99%) nickel(II) sulfate (NiSO4.6H2O, 99 %) were purchased from Fisher Scientific as used as received. Ammonia solution (NH4OH, 95%), iodine (I2, 99.9%); and potassium iodide (KI, 100.5%) from J.T. Baker; hydroxylamine hydrochloride (NH2OH·HCl, 99%) and zinc sulfate (ZnSO4·7H2O, 99.5%) from LabChemie were used as received. Phosphoric acid (H3PO4, ≥85%), monosodium phosphate (NaH2PO4, ≥98%), trisodium phosphate (Na3PO4·12H2O, ≥98%), sodium hydroxide (NaOH, 99%), cadmium(II) nitrate (Cd(NO3)2·4H2O, 99%) from Sigma-Aldrich; disodium hydrogen phosphate (Na2HPO4, 98%) from Scharlau; sodium bisulfite (NaHSO3, 66.9%) from Mallinckrodt Baker; ethanol (C2H5OH, 99.9%) from Merck, potassium bromide (KBr, 99.5%) from Riedel-de-Haen; were all used as received.
Preparation of Starch Hydrogels
An aqueous dispersion of corn starch with a concentration of 0.6173 M of anhydroglucose units (AGU) (10 g of starch in 100 mL distilled water) was prepared. The dispersion was introduced into a three-necked flask and heated at 75 °C for 15 min with gentle agitation. To this dispersion, 200 mL of water were added and cooled down to 60 °C. Then, the established amount of initiator and activator were added to polysaccharide, and the slurry was kept in contact with KMnO4 (8×10−2 M) for 10 min. After this pre-oxidation step, IA monomer (neutralized at 70, 75 and 80% with NaOH or not neutralized), previously dissolved in a volume of 180 mL of distilled water, and MBAm crosslinking agent (only when no neutralized IA was used or neutralized at 75%) were added. Immediately, the final volume was increased up to 500 mL with distilled water and allowed to react for 3 h. Then, the mixture was cooled down and precipitated with ethanol to obtain the modified starch. Finally, the products were washed several times thoroughly with a mixture of 50 % v/v ethanol/water to remove any possible residual monomer and starch soluble fragments. The samples were dried in an oven at 40 °C until constant weight.
Materials Characterization
Infrared spectra of dry samples were obtained using FTIR Shimadzu IR Prestige equipment in KBr pellets.
Sol and gel fractions, Fsol and Fgel, were determined by the Lugol test [40]. Those parameters are defined as follows:
where mi is the initial sample weight and mf is the dry sample after immersion in distilled water at 60 °C during 24 h, and then Lugol test was performed. Determination of carboxyl group content was done following the modified procedure of Chattopadhyay et al. [41]. The mixture of 0.2 g of starch and 2.5 mL of HCI 0.1 N was discreetly stirred for 30 min. Then, it was filtered through a Whatman® qualitative filter paper (Grade 4) and washed with distilled water until no chlorine was detected. The starch was then transferred into a 50 mL beaker, and 30 mL of distilled water was added. Subsequently, the mixture was refluxed during 15 min for the complete starch gelatinization. After that, the system was titrated with NaOH 0.01 N solution using phenolphthalein as indicator. Native starch was used as control and all the measurements were executed by triplicate.
Then, the resulting graft yield, expressed as meq -COOH/100 g starch, was calculated following the Mostafa equation: [42]
Determination of carbonyl group content was carried out following a strategy described in the literature [43]. Starch (0.4 g) in 10 mL of water was transferred into a 50 mL beaker and heated at 100 °C until gelation; then, it was slowly cooled to 40 °C. The pH of the solution was adjusted at 3.2 with HCl 0.1 M and then, 1.5 mL of hydroxylamine hydrochloride was added. Then, the mixture was led at this temperature for 4 h and the excess of hydroxylamine hydrochloride was titrated with HCl 0.1 M to adjust at pH = 3.2. The test was performed by triplicate in each sample.
The WAXS profiles of starches were registered in the reflection mode at 25 °C in a Bruker D8 Advance diffractometer equipped with a Goebel mirror and a PSD (Vantec) detector. Cu-Kα radiation was used and the equipment was calibrated with various standards. A step scanning mode was employed for the detector, with a 2θ step of 0.024º and 0.2 s per step. The WAXS degree of crystallinity, fc, was determined from deconvolution of X-ray profiles into crystalline diffractions and the amorphous halo. In all the analyzed hydrogels the amorphous peak was centered at 2θ of 30.0 ± 0.1º.
The thermogravimetric analysis was performed in TGA Q500 equipment (TA Instruments). The instrument was calibrated in temperature and in weight by standard methods. Dynamic experiments were performed under inert atmosphere at heating rate of 10 °C/min in the temperature range between 40 and 800 °C. The average sample size was ca. 5 mg and the dry nitrogen flow rate was 20 cm3/min. The decomposition activation energy (E a ) of samples was calculated by Broido method [44]. In addition, the thermograms were used to estimate the graft degree [31] of the samples according to the following equation:
Scanning electron microscopy (SEM) characterization of starches was performed using Phillips XL30 equipment working at 25 kV and Au/Pd (80/20) coated samples.
Water adsorption behavior was measured by gravimetry using the tea-bag procedure described by Kabiri et al [45, 46]. Dried sample, ms, 50 mg, placed in a tea bag was immersed in aqueous solution at different pHs, ranging from 2 to 11. The water uptake (H) was measured at different time intervals using the following equation:
where mih and mfh are the initial and final weight including the tea bag, respectively, and Fc is the correction factor for the possible adsorption from the tea bag; being mb and mbh the weight of dry and wet tea bag, respectively, and n the number of replications (n = 5).
Atomic absorption spectrometer Perkin Elmer PE 3030 was used to follow the ability of starches to adsorb metal ions from the amount of residual metal ion in the solution. Ion aqueous solutions of Pb2+ (0.37 mmol/L), Cd2+ (0.90 mmol/L), Zn2+ (1.52 mmol/L), and Ni2+ (1.70 mmol/L) were prepared in a total concentration of 100 mg/L. To 25 mL of each ion solution, 50 mg of polymer were added and, previous to adsorption experiments, slowly and gently shook during 24 h at slow rate and at room temperature. Likewise, the effect of pH variation on the adsorption ability of samples in water solutions was also evaluated for Ni2+ and Pb2+ ions. The pH values of 2.5, 3.5 and 4.5 in the solutions were obtained by adjusting with H2SO4 and HNO3 0.01 M. The adsorption isotherms were measured at 15, 30 min, 1, 2, 4 and 24 h.
Results and Discussion
Preparation of Grafted Starch Hydrogels
Graft polymerizations of IA onto starch, S-g-IAx, were performed by free radical polymerization using KMnO4/NaHSO3 redox system as initiator ([I] = 8 × 10−3 M). As mentioned above, this redox system does not hydrolyze the starch and is suitable for the copolymerization reaction. In Table 1 are collected the percentage of carbonyl and carboxyl groups of the samples obtained at the different reaction conditions as well as the monomer and initiator concentrations used in each reaction.
From the carbonyl content it can be established that the starch was effectively pre-oxidized and the graft reaction occurred throughout the intermediate aldehyde starch. Interestingly, the carboxyl groups decreases as monomer concentration increases (S-g-IA_0.42[IA], S-g-IA_0.66[IA] and S-g-IA_1[IA]) from 0.24 to 0.12. This decrease of carboxyl groups is more pronounced when the monomer is neutralized (S-g-IA_70 N, S-g-IA_75 N and S-g-IA_80 N). The same occurs when the cross-linked agent is used. However, when the ratio of initiator is 3/4 of the initial, named S-g-IA_3/4[I] (6 × 10−3 M), an increment of groups is produced. Moreover, when is initiator concentration is half of initial concentration, named S-g-IA_1/2[I], the amount of these groups decreases with respect to the previous one but is still higher than the percentage of the grafted starch with the initial initiator concentration of 8 × 10−3 M, S-g-IA_1[IA]. Nevertheless, in all the cases, the carboxyl content increases in comparison to native starch, indication of graft polymerization. Comparatively, the carboxyl content is higher when MBAm is incorporated, named CL when no neutralized monomer is used and CL-75 N when the monomer is neutralized at 75 %, in comparison with S-g-IA_75 N. In the first case is 0.14 against 0.12 and in the second is 0.12 against 0.09, see Table 1.
Characterization of Graft Copolymers
Itaconic acid grafting into native starch was analyzed by FTIR measurements (see Fig. 1a). The characteristic regions, i.e. the fingerprint region, 800–1500 cm−1, the C–H stretch region between 2800 and 3000 cm−1, and finally the O–H stretch region between 3000 and 3600 cm−1 are observed. Starches also exhibited complex vibrational modes at low wavenumbers (below 800 cm−1) due to the skeletal mode vibrations of the glucose pyranose ring. The band at 1640 cm−1 characteristic of water adsorbed in the amorphous regions of starch [47] is observed as well as a small shoulder around 1730 cm−1 due to carboxylic acid C=O stretching and ca. 1630 cm−1 corresponding to C–O–H in-plane bending due to itaconic acid grafting.
Figure 1b shows the WAXS profiles of native starch and grafted starch synthesized using half of the initial initiator concentration and 500 mL of volume of pre-oxidation instead of 300 mL, named S-g-IA_1/2[I]b. It is easily observed the A-type crystalline structure of NS, typically found on cereal starches [10, 48]. The pattern reveals the characteristic peaks of this structure with strong reflections at 2θ about 15º and 23º, and an unresolved doublet at 2θ = 17º and 18º [48–51]. The relative percentage of crystallinity [34] previously calculated by our group for NS, 28.3 %, slightly varies with the incorporation of itaconic acid monomer, giving rise to an increment of the amorphous phase. The peaks appear broader and gentler after grafting process, indicating the loss of crystallinity [52–54]. The hydrogen bonds between molecules are weakened and, thus, the thermoplasticity of IA grafted starches increased. As mentioned, the crystallinity of grafted copolymer decreases up to 22 %. The grafting reaction disrupts the intra- and intermolecular bonds between hydroxyl groups present on the starch, which are the responsible of the crystalline structure of NS [13, 55, 56]. However, the incorporation of itaconic acid does not completely destroy the crystalline structure of starch. Besides, the broad peak located near 20º, which can be attributed to V-type (single helix) structures of amylose, seems to be more noticeable due to the decrease of A-type crystal structure.
Figure 2 shows the microscopy analysis of native starch as well as grafted copolymers. Native starch presents a bimodal distribution of grains, typical from cereal starches, with medium particle size ranging from 10 to 20 μm and small sizes from 5 to 10 μm [57–59]. The granules are smooth and irregular, varying from spherical to polygonal, with higher proportion of the latest, which is characteristic of corn starch [59, 60]. In the case of grafted copolymers, i.e. S-g-IA_1/2[I]b and S-g-IA_3/4[I], there are considerable changes in the morphology of these grains, indicating the modification process [61, 62]. The aggregation of granules because of the binder of hydroxyl groups, to form hydrogen and covalent bonds between starch chains, allows the formation of adequate pores for water absorption [62].
Thermal Behavior
The thermal behavior of starches was studied by thermogravimetric analysis. In Fig. 3 the degradation curves carried out at 10 °C/min under inert nitrogen atmosphere of NS and S-g-IA_3/4[I] grafted copolymer are displayed. As occurs in polysaccharides, there are two different stages clearly observed; the first one corresponds to the loss of water associated to its hygroscopic character, and the second step corresponds to the depolymerization of natural polymer with mainly elimination of water and CO2 [31, 56, 63–65]. The sharp peak found in NS is also found in the grafted starches. However, it is also observed the presence of a small step at lower temperatures. This corresponds to the decarboxylation reaction of grafted poly(itaconic acid), which exhibits low stability [27–29]. In spite of this, the grafting is not enough to completely destabilize the starch main chain. The main peak of degradation is observed with a slightly shift to higher temperatures, (see also Table 2).
Considering the equation of Broido [44] as:
where Ea is the activation energy and w is the sample weight at defined time, while w0 and w∞ are the initial and final weights, respectively. From the slope of the logarithmic representation of these parameters, the activation energy can be determined. The thermal degradation process of modified starches is less favorable than in native starch, probably as a consequence of the increase of carboxyl groups’ content (see Ea values in Table 2) [66]. Therefore, the incorporation of itaconic acid gives globally more stability to the starch.
Water Uptake Behavior
The results of water uptake behavior of copolymers in water and saline solutions as a function of grafting degree and gel fraction are collected in Table 3. In water, the hydrogels with higher swelling capacity are those obtained with lower initiator concentration (S-g-IA_1/2[I]) and with lower initiator and reactant contents in the pre-oxidation step (S-g-IA_1/2[I]b). The crystallinity disruption, therefore, the increase of amorphous regions after grafting reaction favors the water uptake [67]. The lowest values are found for copolymers with lower concentration of IA, i.e. S-g-IA_0.42[IA] and S-g-IA_0.66[IA], showing an increment of swelling with the monomer concentration as well as with the diminishment of grafting. This is because itaconic acid is a diprotic acid, so high degrees of grafting implies an increase of possible inter and intramolecular hydrogen bonds, e.g. high crosslinking, which impedes the swelling. Likewise, the decrease on initiator concentration causes diminishment on the grafting degree, so an increase on the water uptake capability. The preparation of copolymer in a large volume, S-g-IA_1/2[I] versus S-g-IA_1/2[I]b, generates a competition between grafting and crosslinking reactions, provoking an increase of water sorption.
Next, the neutralization effect was evaluated, revealing that the increase provokes similar or higher gel fractions, which means that the hydrolysis is not favored. Moreover, the neutralization allows reaching higher values of water uptake. On the contrary, the introduction of crosslinking agent, MBAm, to the reaction, samples CL and CL-75 N, produces a decrease on the gel fraction and degree of grafting, increasing the starch hydrolysis. Specifically, higher water uptake is achieved for S-g-IA_1[IA] in comparison with CL. In the case of neutralized samples, S-g-IA_75 N, its swelling behavior is greater than that of CL-75 N as well as its gel fraction (93.0 vs. 72.8 %) and grafting degree (2.1 vs. 1.5 %).
As summary, it can be said that these copolymers present a polyelectrolyte behavior in water. This performance is also found in the majority of grafted starches in saline solution, since the increment of ionic strength exerts a reduction on water uptake ability. However, the contrary effect is clearly observed when the monomer concentration augments, S-g-IA_0.42[IA], S-g-IA_0.66[IA] and S-g-IA_1[IA], that is the water uptake increases. This may be due to an exchange between Na+ cations and H+ protons of hydrogel, which allows higher water content to be introduced.
Figure 4 displays the kinetics of water uptake of all the obtained systems. In all the cases, the swelling equilibrium is reached after ca. 2 h. However, anomalous swelling behavior is found in some copolymers. At the beginning of the swelling process, the curves exhibit a maximum in the water uptake after which the swelling gradually decreases to an equilibrium value at longer times. This is described in the literature as the overshooting effect [68–70]. Initially, this effect was described taking into account the glassy state of the polymer, which induces a moving rigid core during swelling [71, 72]. Moreover, the kinetic was also interpreted as a consequence of an autocatalytic process of the water penetration into the gel. Other authors established that the overshooting effect might be a consequence of a spontaneous rearrangement of the gel structure on the dynamic swelling [69]. Recently, the phenomenon was also observed in acid solution where pH is lower than pKa of hydrogels obtained by graft crosslink copolymerization of sodium alginate (SA) and acrylic acid (AA) using MBAm as crosslinker. This effect is interpreted as a cooperative physical crosslinking caused by the hydrogen bond formation between the carboxyl groups of the hydrogels in a hydrophobic environment [70]. As can be observed in Fig. 4a the swelling increases as concentration of monomer does. Likewise, the increase on neutralized monomer provokes an augment on the water uptake ability (see Fig. 4b). Figure 4c represents the swelling curves of copolymers as a function of initiator concentration, showing a decrease on the water adsorption capacity as the initiator concentration increases.
Subsequently, the effect of pH on the swelling behavior was studied. As an example, Fig. 5 represents H∞ in water for S-g-IA_1/2[I]b, S-g-MA_75 N and S-g-MA_80 N copolymers as a function of pH at room temperature. At low pH values the maximum of water uptake is low because there is an increment on the protonation of carboxylic groups; whereas the uptake is higher when the pH increases above pKa. The number of charges increases in the network, generating anionic units, which induce electrostatic repulsions within macromolecular chains. This fact produces a higher expansion of the network and then, of the swelling ability [70, 73, 74]. In the case of grafted copolymers with neutralized monomer, there is also a maximum near neutral pH, but after it the hydrogel shrinks. This is because the ionization of the ionizable component is completed and then, the swelling process stops. Thus, the pH augment only increases the ionic strength [75].
Heavy Metal Adsorption
The ability of these itaconic acid grafted starches to remove heavy metals from aqueous solutions was evaluated by atomic absorption spectrometry. The amount of Cd2+, Ni2+, Pb2+ and Zn2+ ions retained by the material expressed as the ratio of adsorbate mass per adsorbent mass, q e , as well as values of the partition coefficient, k d, and the retention capacity, Q r , was determined in all the samples, and the results are collected in Table 4. Metal adsorption becomes regulated by the ion charge, hydrodynamic radius and the characteristics of the material and normally the hydration is inversely related to the ionic radius and this follows Pb2+>Cd2+>Zn2+>Ni2+.
Interestingly, the removal capacity of copolymer increases as higher amount of itaconic acid is grafted [15]. The copolymers with higher removal capacity are those with lower concentration of initiator, S-g-IA_1/2[I]b, which also presents the highest swelling capacity. On the contrary, the lowest found values are for S-g-IA_1[IA] with 8.4 mg/g in the removal of Zn2+ and 8.2 mg/g for Cd2+. The removal activity is related to the material crosslinking, the amount and disposition of acid groups, among other factors related to the nature and properties of adsorbent.
Another parameter that influences the ability to remove metals is the pH medium because the pH of the solution determines the ionic state of the metal as well as of the functional groups at the surface of adsorbent [76–78]. In this work, the capacity of remotion as a function of pH was studied for two ions, nickel and lead, and three copolymers (S-g-IA_1[IA], S-g-IA_80 N and S-g-IA_1/2[I]b, which present proper suitability as seen in Fig. 4. Figure 6 displays the amount of ions adsorbed per gram of S-g-IA_1[IA], S-g-IA_80 N and S-g-IA_1/2[I]b hydrogels as a function of pH. As expected, there is an increment on the ability to remove ions as increasing pH, since exists higher amount of ionized carboxylic groups able to adsorb larger amount of ions [79, 80]. It is also noticeable that in the near to itaconic acid pKa (~3.8), there is a slight slowdown in the uptake, due to there is the same concentration of carboxylate and carboxylic groups.
Competitive Adsorption of Metals
The selectivity of S-g-IA_1[IA], S-g-IA_80 N and S-g-IA_1/2[I]b for all the metals was measured in the same conditions that above and the metal amount in the solution after contact with each starch is depicted in Fig. 7. As can be observed, S-g-IA_80 N and S-g-IA_1/2[I]b follows the trend: Pb2+>>Ni2+>Cd2+>Zn2+ whereas S-g-IA_1[IA] presents this tendency Pb2+>>Zn2+>Cd2>Ni2+. In all the cases Pb2+ is the ionic specie more easily removed and that it follows the same trend that when only one metal is tested.
Isotherms and Kinetics of Adsorption
The equilibrium isotherms of adsorption are crucial to describe the interactions between analyte or adsorbate and sorbent. The respective sorption equilibrium are usually described by the well-known Langmuir or Freundlich relationships [81]. Freundlich equation, which is applied for multilayer adsorption on heterogeneous adsorbent and assumes that the adsorption sites increase exponentially with respect to the heat of adsorption, is described as \(q_{e} = KC_{e}^{1/n}\). where K and 1/n are constants related to adsorption capacity and adsorption intensity, respectively. If the value of 1/n is higher than 1, the adsorption process is feasible and favorable [18].
In the present work, Fig. 8 represents, in their exponential and linear forms, the adsorption equilibrium for Pb2+ and Ni2+ ions as a function of S-g-IA_80 N and S-g-IA_1/2[I]b equilibrium concentrations (Ce), respectively. As it can be observed, both systems follow the Freundlich equation. Resulting values of K and 1/n of 8.7 × 10−6 (mg/g)(L/mg)1/n and 0.29 for Ni2+ and 56.5 × 10−3 (mg/g)(L/mg)1/n and 0.62 for Pb2+, respectively, indicating that the adsorption processes in both systems are favorable.
Besides, adsorption time is an important parameter because this factor can reflect the adsorption kinetics of an adsorbent for a certain initial concentration of the adsorbate. The effect of adrption time on the adsorption curves of Pb2+ and Ni2+ ions by S-g-IA_80 N and S-g-IA_1/2[I]b, respectively, are represented in Fig. 9. The adsorption rate is very fast during the first 5 min of the process, during this period the respective removals of Ni2+ and Pb2+ are 12.9 and 5.1 mg/g for S-g-IA_80 N and S-g-IA_1/2[I]b, respectively. In both cases, after this period, the adsorption rate is slow down and adsorption equilibrium is gradually achieved within 50 min, in which the respective removals of Ni2+ and Pb2+ reached values of 12.9 and 9.6 mg/g for S-g-IA_80 N and S-g-IA_1/2[I]b, respectively. Both curves fit very well with the pseudo-second order kinetics (see plots 9B, 9D).This model [82] is based on the plotting of t/q(t) against t (see the following equation), which should give a linear relationship, where t is time and q(t) is the total adsorbed amount at time t.
In this case, \(q_e^C\) is treated as an adjustable parameter; this made possible to compare its values with the real values, and k 2 is the so-called pseudo-second order constant.
In the current work, k 2 calculated values are 0.11 g/mg min for Ni2+ and 1.5 × 10−2 g/mg min for Pb2+ adsorption. The \(q_e^C\) calculated values are 12.8 and 9.6 mg/g, while experimental obtained values are 12.8 and 9.7 mg/g, respectively for Ni2+ and Pb2+ adsorption processes. These values demonstrate the validity of this model and that the removal from a solution is due to physicochemical interactions between the metal ion and the starch, being the surface adsorption that involves chemisorption/quelation the rate-limiting step.
Conclusions
New hydrogels were obtained by graft copolymerization of starch with itaconic acid using mild redox conditions. The grafting was characterized by several techniques, such as FTIR, WAXS and TGA. The swelling behavior was enlarged with the increase of IA monomer content and the monomer neutralizing degree, without the crosslinking addition and with the diminishment of initiator and reactants in the pre-oxidation step. The water uptake of some of these grafted starches was around 1800 %. In addition, the swelling behavior showed pH dependence. These hydrogels were able to adsorb heavy metals with preference for lead, as follows Pb2+>>Ni2+>Zn2+>Cd2+. The experimental data was fitted to Freundlich adsorption isotherm and the pseudo-second order kinetic model. In summary, these biopolymeric materials based on starch and itaconic acid can be satisfactorily used as adsorbent for removal of water contaminants and their preparation does not require potent and contaminant redox systems.
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Acknowledgments
Authors thanks Consejo de Desarrollo Científico y Tecnológico (CONDES) of Universidad del Zulia for the financial support (Project VAC-CONDES-CC-0136-14). A. Muñoz-Bonilla thanks MINECO for her Ramon y Cajal contract.
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Soto, D., Urdaneta, J., Pernia, K. et al. Itaconic Acid Grafted Starch Hydrogels as Metal Remover: Capacity, Selectivity and Adsorption Kinetics. J Polym Environ 24, 343–355 (2016). https://doi.org/10.1007/s10924-016-0780-9
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DOI: https://doi.org/10.1007/s10924-016-0780-9