Adsorption kinetics of methylene blue from wastewater using pH

Scientific Reports volume 13, Article number: 11900 (2023) Cite this article 458 Accesses 5 Altmetric Metrics details In this work, starch/poly(acylic acid) hydrogels were synthesized through a free

Scientific Reports volume 13, Article number: 11900 (2023) Cite this article

458 Accesses

5 Altmetric

Metrics details

In this work, starch/poly(acylic acid) hydrogels were synthesized through a free radical polymerization technique. The molar ratios of acrylic acid to N,N′-methylenebisacrylamide were 95:5, 94:6, and 93:7. The samples exhibited an amorphous porous structure, indicating that the size of the pores was contingent upon the amount of cross-linking agent. The quantity of acrylic acid in structure rose with a little increase in the amount of the cross-linking agent, which improved the hydrogels’ heat stability. The swelling characteristics of the hydrogels were influenced by both the pH level and the amount of cross-linking agent. The hydrogel with a ratio of 94:6 exhibited the highest degree of swelling (201.90%) at a pH of 7.4. The dominance of the Fickian effect in regulating water absorption in the synthesized hydrogels was demonstrated, and the kinetics of swelling exhibited agreement with Schott's pseudo-second order model. The absorption of methylene blue by the hydrogels that were developed was found to be influenced by various factors, including the concentration of the dye, the quantity of the cross-linking agent, the pH level, and the duration of exposure. The hydrogel 95:5 exhibited the highest adsorption effectiveness (66.7%) for the dye solution with a concentration of 20 mg/L at pH 10.0. The examination of the kinetics and isotherms of adsorption has provided evidence that the process of physisorption takes place on heterogeneous adsorbent surfaces and can be explained by an exothermic nature.

Researchers have become interested in starch-based hydrogels because of wide range of useful properties including biocompatibility, biodegradability, physiochemical properties, high efficiency, and reasonable price1. Hydrogels derived from starch are utilized in a wide range of industries including the environment, agriculture, medicine, absorbents, and so forth2. Dye adsorption by these hydrogels in industrial wastewater is one of their many potential uses that has garnered a lot of attentions. Organic dyes are used in numerous industries, including textiles, prints, plastics, and cosmetics, but they are extremely hazardous to water supplies and ecosystems3. Aromatic organic dyes, like methylene blue (MB), are more toxic and stable than other types of organic dyes; they can also cause nausea, vomiting, tissue necrosis, and nerve damage in humans4. Dye separation can be accomplished through a variety of processes, including sedimentation5, ion exchange6, coagulation7, filtration8, and adsorption9, 10. Adsorbents are superior to other methods by having advantages such as recyclability, low cost, high absorption efficiency, flexibility in performance, efficiency and simple handling11.

Despite the different advantages of starch-based hydrogels, weaknesses such as low mechanical resistance and high sensitivity to degradation have prevented their widespread use in industry12. Starch can be modified via physical13, chemical14, blending15, and enzymatic16 techniques to solve the aforementioned issues. Oxidation17, hydrolysis18, esterification19, and grafting20 are among the methods of modifying starch chemically. Chemical grafting with vinyl monomers such as acrylic acid has gained interest due to the precise control over the modification process, greater adsorption capacity, and creating a more stable and uniform product21. Furthermore, grafting hydrogel with poly(acrylic acid) (PAA) improves properties for instance mechanical strength, thermal resistance, and ability to absorb water, as well as broadening its application22, 23. Introducing negative charges to starch is essential for the adsorption of ions or positively-charged dyes by starch-based hydrogels. Starch oxidation and modification with poly(acrylic acid) are two methods used for this purpose24. While starch oxidation may alter the starch structure and gelation properties, modification of starch with poly(acrylic acid) offers advantages such as a simplified process, enhanced water absorption capacity, tunable properties, and improved stability. This method effectively reduces costs and addresses potential environmental concerns associated with the modification process25, 26. Several factors, such as temperature, pH, dye concentration, and crosslinking agent can influence the adsorption efficiency of hydrogels27. The addition of N,N′-methylenebisacrylamide (MBA) as a crosslinker to starch hydrogel brings numerous benefits, including the facilitation of a stable structure formation, improved structural integrity, enhanced water absorption capacity, and the ability to tailor porosity, swelling behavior, and mechanical properties28. This versatility makes the hydrogel an exceptional choice for diverse applications in agriculture, biomedicine, and beyond29.

Introducing an innovative and sustainable method, this study synthesizes starch-based hydrogels grafted with poly(acrylic acid), offering a cost-effective and eco-friendly approach. This sustainable approach provides simplicity and affordability, making it highly practical for large-scale production. The investigation delves into the fascinating characteristics of these hydrogels, exploring their unique swelling behavior, adsorption kinetics, and isotherms. Remarkably, the results unveil their remarkable potential as exceptionally efficient adsorbents for dye removal. By optimizing key factors, including cross-linking agent concentration, these hydrogels demonstrate enhanced performance, opening doors for various applications in wastewater treatment and environmental remediation. This research sheds light on the intricate mechanisms of dye adsorption, advancing the field of sustainable materials. Merging principles from green chemistry, materials science, and environmental engineering, the study propels the utilization of starch-based hydrogels as eco-friendly alternatives with exceptional adsorption capabilities, revolutionizing the treatment of hazardous organic dyes in industrial wastewater.

Starch from potato, ceric ammonium sulfate (CAS, ≥ 94%), N,N′-methylenebisacrylamide (MBA, 99%), acrylic acid (AA, 99%), and methylene blue (MB) were purchased from Sigma-Aldrich.

A single-necked flask was filled with starch (1 g), distilled water (5 mL), and MBA and stirred under nitrogen at ambient temperature. The reaction solution was mixed with CAS as initiator, and AA, and the temperature was raised to 70 °C. Finally, the mixture was poured into a teflon mold and reaction was continued for 48 h at 60 °C. To evaluate the influence of the amount of crosslinker on the final properties, three samples, S-AA-1, S-AA-2, and S-AA-3 were prepared with different molar ratios of AA to MBA (95:5, 94:6, and 93:7, respectively). The weight ratio of starch and acrylic acid was 1:1. The selection of the 1:1 starch to acrylic acid ratio in our hydrogel synthesis was driven by the objective of balancing the structural integrity and sustainability of the gel. Alterations in the amount of acrylic acid had a direct impact on the concentration of the cross-linking agent, MBA, as it depends on the acrylic acid content. Decreasing the amount of acrylic acid resulted in reduced MBA concentration, leading to insufficient firmness and a propensity for collapse in the resulting hydrogel. Conversely, increasing the amount of acrylic acid posed a challenge to the sustainability of the hydrogel. To strike a compromise between gel stability and sustainable properties, we opted for the 1:1 ratio as the most suitable choice.

Fourier-transform infrared spectroscopy (FTIR) of hydrogels combined with potassium bromide pellets was investigated in the 400–4000 cm−1 range using a Bruker Tensor 27 FT-IR Spectrometer manufactured in Germany. Using an X-ray diffractometer (EQUINOX3000, Inel, France) with 40 kV voltage, 30 mA current, and Cu Kα radiation, the crystallinity characteristic was examined. Under a nitrogen atmosphere, samples were heated from 25 to 600 °C at a heating rate of 10 °C/min to ascertain their thermal stability using thermogravimetric analysis (TGA) (Q600, TA, USA). Field Emission Scanning Electron Microscope (FE-SEM) (MIRA3 FEG-SEM, Tescan, Czech) operating at 30 kV was utilized to examine the morphology of the synthesized samples. The water-swollen samples were freeze-dried for 48 h using a freeze dryer (Martin Christ, Germany). The samples were then covered in gold to make them more conductive. The size of hydrogel pores was determined using ImageJ software. A portion of the synthesized samples was placed in 100 mL distilled water with specific pH values to examine swelling properties. Four pH values were specifically chosen to investigate the swelling and absorption behavior of starch/poly(acrylic acid) hydrogels: an acidic pH of 2.0, a pH close to the pKa of acrylic acid (4.8), a neutral pH of 7.4, and an alkaline pH of 10.0. At specific intervals, samples were weighed and measurement was repeated until the sample weight was fixed. The swelling ratio percentage was calculated with Eq. (1)30.

where Q, Mt and M0 are the percentage of water absorption (gwater/gabsorbent), sample weight at time t (g), and initial sample weight (g), respectively.

To evaluate the effectiveness of hydrogel in absorbing MB at room temperature and pH values of 2.0, 4.8, 7.4, and 10.0, 0.05 g of hydrogel was immersed in MB solution. At certain intervals, 1.5 mL of the aqueous solution was removed and replaced with distilled water. MB solution was made at concentrations of 2, 3, 4, 5, 10, and 20 mg/L to investigate the effect of dye concentration on adsorption kinetics. A UV/visible spectrophotometer (Hanon, China) at 665 nm for pH 2.0, 663 nm for pH 4.8, 665 nm for pH 7.4, and 667 nm for pH 10.0 was utilized for determining MB concentration. Hydrogel absorption capacity (qe, mg dye/g hydrogel) and dye adsorption efficiency (E, %) were calculated using Eqs. (2) and (3), respectively21.

where Ci, Ce, V, and m are the initial concentration of MB solution (mg/L), the concentration of the MB solution after adsorption (mg/L), the volume of the solution (mL), and the mass of the adsorbent (g), respectively.

To further comprehend the adsorption mechanism, the adsorption kinetics were investigated using pseudo-first order (PFO), pseudo-second order (PSO), and intraparticle diffusion (IPD) models, as indicated by Eqs. (4)31, (5)32, and (6)33.

where qe, qt, t, k1, k2, k3, and C are respectively the adsorption capacity of the adsorbent in the equilibrium state (mg/g), the adsorption capacity of the adsorbent at time t (mg/g), time (h), the rate constant of the PFO equation (h−1), the rate constant of the PSO equation (g/(mg h)), the rate constant of the IPD ((mg/g)/h), and a constant associated with the thickness of the boundary layer (mg/g). Furthermore, the initial adsorption rate (mg/(g h)) in the PSO model can be determined using Eq. (7)34.

Langmuir (Eq. (8))35, Freundlich (Eq. (9))36, and Temkin (Eq. (10))37 adsorption isotherms were analyzed using experimental data to define the interaction between the adsorbed substance and the adsorbent.

where Ce, qe, qm, KL, n, KF, R, T, b, and KT are the concentration of MB solution in the equilibrium state (mg/L), the adsorption capacity of the adsorbent in the equilibrium state (mg/g), the maximum capacity of adsorption (mg/g), the Langmuir adsorption constant (L/mg), the Freundlich dimensionless constant indicating adsorption intensity, the Freundlich adsorption constant (mg/g), the temperature (K), the heat of adsorption (kJ/mol) and the Temkin adsorption constant (L/g), respectively.

Herein, starch/PAA-based pH-sensitive adsorbents with different amounts of crosslinker have been prepared by solution graft polymerization of PAA onto starch using CAS as initiator and MBA as crosslinker. Figure 1 depicts the polymerization mechanism to prepare hydrogels.

Synthesis of starch/PAA-based hydrogels.

Evaluation and confirmation of hydrogels based on starch were performed using FT-IR, XRD, TGA, and FE-SEM analyses. Figure 2a depicts the FTIR spectra of starch and starch/PAA-based hydrogels. The individual peaks of starch occurred at wavenumbers of 3434 cm−1, 1028 cm−1, and 1644 cm−1, corresponding to O–H stretching, C–O–C asymmetric stretching vibration, and C–O bending associated with OH group, respectively. Furthermore, the peaks appearing at 1307 cm−1, and 1412 cm−1 are related to C–H angular38. In the hydrogel samples, in addition to the peaks of starch, a peak at 1735 cm−1 is attributed to the stretching of the carbonyl groups of PAA which implies that PAA has successfully bonded to starch. At 2941 cm−1, C–H stretching of PAA and starch was also detected39. Figure 2b depicts the XRD patterns of starch and synthesized hydrogels. Starch characterization peaks were at 2θ = 15.2° (101), 18.0° (100), and 23.3° (110). To assess the effect of the degree of crosslinking during the synthesis of different hydrogel samples, a comparison of the percentage of crystallinity between starch and PAA-based hydrogels was performed using XRD. The percentage of crystallinity of pure starch was determined to be 37.8% using the ratio between the area under the diffraction peaks and the total area of the entire XRD pattern. In the XRD pattern of starch/PAA-based hydrogels, a broad peak without starch characterization peaks was observed, indicating the amorphous structure of the hydrogel samples40. The researchers also reported the disruption of the starch crystal structure through the process of PAA grafting onto starch41. Because of intramolecular and intermolecular hydrogen bonding, starch has a highly ordered crystalline structure. The steric hindrance of similar charges generated by the interaction of starch OH groups with COO− of PAA limited the mobility of starch chains in hydrogel samples. As a result, the formation of intermolecular hydrogen bonds in starch was reduced, causing the starch crystal structure to disintegrate and the crystalline phase to be destroyed42.

FTIR spectra, XRD patterns, and TGA thermograms of starch and starch/PAA hydrogels.

TGA was utilized to assess thermal stability (Fig. 2c, Table 1). The analysis indicates a two-stage degradation of hydrogels. The first step of decomposition at 182–320 °C is related to breaking the C–O–C bonds of the main chain of starch and the dehydration of the saccharide ring. The second degradation stage is associated with the decomposition of PAA grafted to starch at 320–520 °C43. The percentage of grafted acrylic acid was determined using Eq. (11) and reported in Table 144:

where W1 and W2 are weight loss in stage 1 and stage 2, respectively. By increasing the amount of crosslinking agent, the amount of grafted acrylic acid to the hydrogel structure was increased. The drop in WLmax and increase in Td50 with increasing crosslinking agent indicated a partial enhancement of in thermal stability which was caused by the increased activation energy required to destroy samples with higher crosslinking agents45.

The bulk morphology of the hydrogels were examined using FE-SEM (Fig. 3). All three samples demonstrated the porous structure which provides sites for solution diffusion into the polymer network and interaction of external stimuli with the polymer network. Grafting of PAA to starch enhances surface roughness and creates folds. Folds have a higher specific surface area than starch, facilitating water diffusion into the polymer network46. The average size of pores in the S-AA-1, S-AA-2, and S-AA-3 samples was 22.9, 17.1, and 14.5 µm, respectively, indicating that pore size decreased with increasing crosslinker which is attributed to increased hydrogel elasticity, which depends on the crosslinking density47. Moreover, existence of larger pores decreases transportation resistance and enhances water absorption capacity48.

FE-SEM images of the surface of hydrogel samples S-A A-1 (a,d), S-AA-2 (b,e), and S-AA-3 (c,f) at ×500 and ×250 magnification scale.

Figure 4 illustrates the equilibrium swelling (Qe) and swelling behavior of the samples across a range of pH values. All the samples showed a dramatic swelling in the initial times and then reached equilibrium. The pH affects the behavior of ionic hydrogels. In the synthesized samples, grafting of PAA to starch caused in the induction of a significant number of negatively-charged COO− groups. The results revealed that swelling increased as the pH varied from 2.0 to 7.4 whereas it decreased at pH = 10.0 and maximum swelling was observed at pH = 7.4. Carboxylate groups are protonated in an acidic environment, resulting in hydrogen bonding between polymer chains which act like physical crosslinks and lead to polymer network shrinkage and decreased swelling. Deprotonation of the carboxylic groups occurs when the pH is greater than PAA's pKa which results in swelling due to electrostatic repulsions between chain segments49. At pH = 10.0, protecting Na+ cations in NaOH solution from COO− groups inhibited the complete anion-anion repulsion in hydrogels, resulting in reduced water absorption50. The observed trend regarding the impact of pH on the swelling behavior aligns with existing literature. However, it should be noted that the hydrogels synthesized in this study exhibited a notably higher rate of swelling51, 52. Furthermore, a comparison of Qe of S-AA-1 and S-AA-2 at every pH revealed that Qe increased at higher crosslinking agent concentration. Increased cross-linking results in the formation of a three-dimensional structure in the polymer network, allowing water to permeate the hydrogel structure more effectively53. However, comparing Qe for S-AA-2 with S-AA-3 showed that Qe decreased with increasing crosslinker due to increased crosslinking density among polymer chains, which causes the creation of a stiffer structure that prevents more water from entering the structure53.

Swelling properties of starch/PAA hydrogels at pH 2.0, 4.8, 7.4, and 10.0.

The modified power law equation, Eq. (12), was used to understand the water transport mechanism into the hydrogel52.

where Mt and Me are hydrogel weight at time t (g) and maximum hydrogel weight (g), respectively. The k is a proportionality constant, and n is a description of the type of diffusion mechanism. The equation is limited to 60% of absorbed water, which corresponds to a linear response of water absorption to swelling time. Type of water diffusion in the hydrogel is identified based on the range of n. n is calculated and given in Table 2 by plotting ln (Mt/Me) versus time. Results indicated that for all the synthesized hydrogels n is < 0.5, indicating Fickian diffusion, which signifies that diffusion is the water absorption control mechanism. Schott's pseudo-second order swelling kinetic model, (Eq. (13)), was used to determine the swelling kinetics from results obtained54.

where St, Sth, and kis are the swelling ratio at time t, the maximum theoretical swelling ratio, and the initial swelling ratio constant, respectively. By plotting t/St versus t and calculating the slope and intercept, Qth and kis were calculated (Table 2). The pseudo-second order swelling kinetic model governs the swelling procedure, as evidenced by the excellent agreement of theoretical Qth data with experimental data and the achievement of R2 > 0.9800. The variation of kis with pH is similar to the variation of Q with pH and is determined by the rate of relaxation of polymer chains in the polymer network. The ionization of carboxylate groups and electrostatic repulsions occurred as the pH increased from 2.0 to 4.8, leading to enhanced polymer chain relaxation. This phenomenon increased with increasing pH up to 7.4. Rapid relaxation facilitates the ability for water molecules to permeate the polymer network, thereby accelerating the rate of swelling. At pH = 10.0, the decrease in the mobility of polymer chains due to the screening effect of Na+ cations resulted in a decline in water diffusion into the polymer network; as a result, kis decreased54.

MB is widely used as a textile dye, but its hazardous contamination poses a concern to human health and safety. Adsorption kinetics of MB by hydrogels is influenced by many factors. The influence of initial MB concentration, time, pH, and crosslinking agent on hydrogel adsorption behavior is investigated in this study. The adsorption capacity of S-AA-1 versus pH is shown in Fig. 5a. The data demonstrated that an increase in pH resulted in enhanced adsorption performance. The same trend was observed for other hydrogels (Fig. S1). At low pH values, the majority of the carboxylic anions in PAA were protonated, resulting in the formation of COOH. As a result, electrostatic repulsion between COO− anions vanished, while hydrogen interactions between polymer chains increased. Ultimately, the structure shrank, making it more difficult for MB molecules to penetrate55. Furthermore, the interactions between the carboxylate ions generated competition between excess dissolved H+ ions and positively-charged dye molecules, resulting in limited adsorption at these pH values21. Adsorption is confined to hydrogen bonds between OH or COOH groups of polymer chains and the amine groups of MB at low pH (below the isoelectric point)55. PAA carboxyl groups were deprotonated and converted into carboxylate ions with a negative charge at high pH values. Electrostatic repulsions between negatively-charged groups in hydrogel resulted in structure expansion and increased electrostatic interactions between negatively-charged groups of PAA and positively-charged groups in MB39. As a result, adsorption increased dramatically. Furthermore, according to the time-dependent adsorption capacity curves, in all cases, adsorption capacity increased versus time, whereas the adsorption rate was initially rapid, then slowed, and finally reached an equilibrium. The availability of active sites explains the rapid adsorption in the early stages. Adsorption efficiency of the adsorbent at various pH levels was investigated in terms of the initial concentration of MB (Figs. 5c and S2). With an increase in the concentration of dye from 2 to 10 mg/L, the efficiency of the adsorbent increased. However, in a solution with a concentration of 20 mg/L, a significant increase compared to the 10 mg/L solution was not observed and reached a constant value. One of the reasons for such behavior could be increased contact between MB molecules and adsorbent, as well as increased driving force to mass transfer56. The literature demonstrates consistent trends regarding the impact of pH, dye concentration, and time on the adsorption of MB by starch-based hydrogels21, 39. In contrast to previous studies, it was observed that the adsorption capacity in the present study was comparatively lower. The diminished adsorption capacity may be attributed to several factors, including the reduced concentration of the dye solution, the influence of the cross-linking agent, and the dimensions of the pores within the synthesized hydrogel. Comparisons of hydrogel adsorption capacity curves were made at pH = 2.0 and an initial concentration of 2 mg/L to ascertain the impact of crosslinker concentration on adsorption behavior (Fig. 5b). S-AA-1 was found to have a greater absorption capacity than S-AA-3. Reducing the size of the pores by increasing the amount of crosslinking agent made dye penetration into the hydrogel network structure more difficult, which could be the reason of this phenomenon. Ighalo and coworkers also documented comparable findings regarding the impact of mesoporous size on both adsorption capacity and adsorption kinetics57.

(a) The influence of pH on S-AA-1 adsorption capacity, (b) The influence of crosslinking agent on the adsorption capacity of synthesized hydrogels, (c) The influence of the initial dye concentration on the adsorption efficiency of hydrogel S-AA-1.

The adsorption mechanism and its rate prediction were studied by utilizing linearized PFO, PSO, and IPD models to examine kinetics. The PFO model assumes physical adsorption, and hydrogen bonding and electrostatic interactions between the adsorbent and dye are the primary mechanisms that regulate the adsorption process. According to this model, the adsorption capacity is proportional to the availability of active sites58. The PSO model is based on chemical adsorption with ionic interactions between the adsorbate and adsorbent, which controls the adsorption rate. In this model, the adsorption rate is proportional to the square of the difference among accessible active sites and occupied active sites at equilibrium39. The IPD model depicts the multi-stage absorption process and includes linear areas with varying slopes59. The obtained results were used to fit the PFO and PSO models (Figs. S3–S10), and the kinetic data are displayed in Tables 3, S1, S2, and S3. The higher R2 of the PFO model compared to the PSO model and the relatively close qe acquired by the PFO model to the experimental qe in the majority of samples at low pH values (2.0 and 4.8) indicated that the adsorption process is completely in line the PFO model at these two pH values. At high pH values (7.4 and 10.0), the difference between the qe obtained from the PSO model with the experimental qe increased, whereas the PFO model still provided a better fit to the experimental data.

Moreover, the IPD model was applied to all the data for a comprehensive description of MB diffusion into the hydrogel (Figs. S11–S14, Tables 4, and S4–S6). All three linear regions for MB adsorption by the synthesized hydrogels had different slopes away from the origin, suggesting that the adsorption is regulated by a multi-step mechanism. The initial step explains the transfer of the dye to the hydrogel's outer surface via diffusion into the boundary layer60. In the second step, MB molecules diffuse continuously into the adsorbent sites in the hydrogel pores via intraparticle diffusion. The third step is the equilibrium of the adsorbent, which occurs when the adsorption capacity has been stabilized and the active sites on the inner surface of the pores are completely saturated with dye molecules21. At a constant pH, k3, the initial rate of absorption, increased for stages 1 and 2 of the IPD model when the dye solution concentration was increased from 2 to 5 mg/L. k3 of the second stage was greater than k3 of the first stage for all samples, indicating that film diffusion is faster than intra-particle diffusion. The same trend was also observed when studying the effect of pH on the constants obtained from the IPD model. In all hydrogels, with increasing pH from 2.0 to 10.0, k3 of the first step and k3 and C of the second step increased. Hydrogel comparisons revealed that sample S-AA-1 has the highest k3 and C, while sample S-AA-2 has the lowest k3 and C.

The equilibrium behavior of the adsorbent and adsorbed molecules was characterized by the Langmuir, Freundlich, and Temkin adsorption isotherms (Figs. S15–S17, Table 5). The Langmuir isotherm indicates monolayer adsorption on homogeneous adsorbent sites, and none of the adsorbate species interact with one another61. The negative slope of the graph of the experimental data fitted with this isotherm and the low value of R2 indicate that the Langmuir isotherm is unsuitable for prepared hydrogels. The Freundlich isotherm is associated with heterogeneous adsorbent surfaces, where adsorption is not uniform. The n parameter is the heterogeneity factor, which indicates the nonlinear relationship between concentration and absorption. If n = 1, the adsorption process is linear; if n < 1, chemical adsorption happens; and if n > 1, physical absorption occurs62. All samples had n values below 1, suggesting that chemical absorption is occurring. It demonstrated the adsorbent's ability to electrostatically interact with MB molecules. The Temkin isotherm is associated with the uniform distribution of energy during the adsorption process, and the interaction between the adsorbent and the adsorbed molecule causes a linear decrease in the adsorption heat for all molecules63. The positive value of bT in the synthesized samples indicated that the adsorption process is exothermic64. Furthermore, the high value of bT in comparison to KT indicates that the adsorbent and the adsorbed have a strong interaction20. In comparison to the other two isotherms, the Freundlich model with the highest R2 value was considered to be the best fit for the empirical evidence.

One of the challenges encountered in the field of adsorption pertains to the mechanism of adsorption. In order to investigate the adsorption mechanism of MB using hydrogels based on starch/PAA and to ascertain the potential interaction between the adsorbent and adsorbate, FTIR spectroscopy was conducted on MB, S-AA-1 prior to adsorption, and S-AA-1 after adsorption (S-AA-1/MB), as depicted in Fig. 6. The spectral peaks associated with the characterization of MB were observed at wavenumbers of 1604 cm−1, 1492 cm−1, 1398 cm−1, and 1246 cm−1. These wavenumbers correspond to the stretching vibration of the aromatic ring, the vibration of the heterocycle skeleton, the symmetric bending vibration of the CH3 groups in the dimethylamine groups, and the CN stretching vibration, respectively65. In the spectral analysis of S-AA-1/MB, alongside the characteristic peaks associated with hydrogel characterization, distinct peaks indicative of MB identification were observed. It is important to point out that there was a slight shift observed in the peaks. Hence, the adsorption of dye by the synthesized hydrogel was confirmed through FTIR analysis. The findings indicate that the likely mechanism of MB adsorption by the starch/PAA hydrogel involves π-π interaction, dipole–dipole hydrogen bonding, and Yoshida hydrogen bonding66. Another potential mechanism for adsorption is the electrostatic interactions between charged groups in the hydrogel and charged groups in MB. This mechanism was verified by investigating the impact of pH on the adsorption capacity. An increase in the number of charged groups led to the generation of a greater number of binding sites within the hydrogel, thereby resulting in an augmented adsorption capacity. Figure 7 illustrates the various mechanisms of MB adsorption on the hydrogel.

FTIR spectra of MB, S-AA-1 and S-AA-1/MB.

Possible adsorption mechanisms of MB onto the synthesized hydrogel.

This study involved the synthesis of sustainable porous starch hydrogels that were grafted with PAA. Three different molar ratios of PAA to MBA (95:5, 94:6, and 93:7) were used in the synthesis process. The purpose of this synthesis was to create hydrogels that could effectively adsorb methylene blue from water through solution polymerization. The introduction of PAA through grafting resulted in the disruption of the crystalline arrangement of starch, leading to the formation of a hydrogel with enhanced thermal stability compared to unmodified starch. The augmentation of the cross-linking agent resulted in a reduction in pore size and an increase in the grafting of PAA onto starch. The investigation into the swelling characteristics of the samples revealed an upward trend between pH levels and swelling, as evidenced by an increase in swelling from pH 2.0 to 7.4. Conversely, an inverse relationship was observed between swelling and pH, indicating a decrease in swelling as pH level increased. The hydrogel with a composition ratio of 94:6 exhibited the highest level of swelling, reaching a maximum value of 201.9%, when tested under a pH of 7.4. The modified Power Law model to investigate the mechanism of water transfer to hydrogel showed that Fickian diffusion controls the adsorption mechanism. Furthermore, the swelling kinetics of the hydrogels that were synthesized adhered to Schott's pseudo-second order swelling kinetic model. The study investigated the impact of various parameters, including pH, dye solution concentration, cross-linking agent quantity, and time, on the adsorption behavior of methylene blue by hydrogels. The observed behavior of increased adsorption capacity, resulting from the increase in pH from 2.0 to 10.0 and the initial amount of dye, can be attributed to two factors: the enhancement of electrostatic interactions and the greater availability of active sites for adsorption. The absorption capacity experienced a decrease as a result of the increased cross-linking factor, which led to a more rigid structure and increased resistance to die penetration. The dye solution with a concentration of 20 mg/L at pH 10.0 exhibited the highest adsorption capacity and adsorbent efficiency (26.7 mg/g, 66.7%) when using a hydrogel with a ratio of 95:5. The analysis of hydrogel experimental data using the pseudo-first order kinetic model and the Freundlich isotherm revealed that physisorption takes place in a non-uniform manner on surfaces of heterogeneous adsorbents. Additionally, the Temkin isotherm study demonstrated that the adsorption mechanism of methylene blue by the synthesized hydrogels exhibits an exothermic nature.

The datasets generated and/or analyzed during the current study are not publicly available at this time as the data form part of an ongoing study. However, the datasets are available from the corresponding author (Mehdi Salami-Kalajahi, [email protected]) on reasonable request.

Qamruzzaman, M., Ahmed, F. & Mondal, M. I. H. An overview on starch-based sustainable hydrogels: Potential applications and aspects. J. Polym. Environ. 30, 19–50. https://doi.org/10.1007/s10924-021-02180-9 (2022).

Article CAS Google Scholar

Al-Aidy, H. & Amdeha, E. Green adsorbents based on polyacrylic acid-acrylamide grafted starch hydrogels: The new approach for enhanced adsorption of malachite green dye, from aqueous solution. Int. J. Environ. Anal. Chem. 101, 2796–2816. https://doi.org/10.1080/03067319.2020.1711896 (2021).

Article CAS Google Scholar

Farhan Hanafi, M. & Sapawe, N. A review on the water problem associate with organic pollutants derived from phenol, methyl orange, and remazol brilliant blue dyes. Mater. Today Proc. 31, A141–A150. https://doi.org/10.1016/j.matpr.2021.01.258 (2020).

Article CAS Google Scholar

Karri, R. R., Ravindran, G. & Dehghani, M. H. Chapter 1—wastewater—sources, toxicity, and their consequences to human health. In Soft Computing Techniques in Solid Waste and Wastewater Management (eds Karri, R. R. et al.) 3–33 (Elsevier, 2021). https://doi.org/10.1016/B978-0-12-824463-0.00001-X.

Chapter Google Scholar

Zhu, M. X., Lee, L., Wang, H. H. & Wang, Z. Removal of an anionic dye by adsorption/precipitation processes using alkaline white mud. J. Hazard. Mater. 207(149), 735–741. https://doi.org/10.1016/j.jhazmat.2007.04.037 (2007).

Article CAS Google Scholar

Joseph, J., Radhakrishnan, R. C., Johnson, J. K., Joy, S. P. & Thomas, J. Ion-exchange mediated removal of cationic dye-stuffs from water using ammonium phosphomolybdate. Mater. Chem. Phys. 242, 122488. https://doi.org/10.1016/j.matchemphys.2019.122488 (2020).

Article CAS Google Scholar

Kasperchik, V. P., Yaskevich, A. L. & Bil’dyukevich, A. V. Wastewater treatment for removal of dyes by coagulation and membrane processes. Petrol. Chem. 52, 545–556. https://doi.org/10.1134/S0965544112070079 (2012).

Article CAS Google Scholar

Liu, Y., Zhu, W., Guan, K., Peng, C. & Wu, J. Freeze-casting of alumina ultra-filtration membranes with good performance for anionic dye separation. Ceram. Int. 44, 11901–11904. https://doi.org/10.1016/j.ceramint.2018.03.160 (2018).

Article CAS Google Scholar

Foroughirad, S., Haddadi-Asl, V., Khosravi, A. & Salami-Kalajahi, M. Synthesis of magnetic nanoparticles-decorated halloysite nanotubes/poly([2-(acryloyloxy)ethyl]trimethylammonium chloride) hybrid nanoparticles for removal of Sunset Yellow from water. J. Polym. Res. 27, 320. https://doi.org/10.1007/s10965-020-02293-0 (2020).

Article CAS Google Scholar

Rawat, S. & Singh, J. Fabrication of iron nanoparticles by reusing an iron waste and their application as efficient adsorbents to remove crystal violet dye from water. J. Appl. Sci. Innov. Technol. 1, 37–46 (2022).

Google Scholar

Foroughirad, S., Haddadi-Asl, V., Khosravi, A. & Salami-Kalajahi, M. Magnetic halloysite-based molecularly imprinted polymer for specific recognition of sunset yellow in dyes mixture. Polym. Adv. Technol. 32, 803–814. https://doi.org/10.1002/pat.5132 (2021).

Article CAS Google Scholar

Kabir, S. M. F. et al. Cellulose-based hydrogel materials: Chemistry, properties and their prospective applications. Prog. Biomater. 7, 153–174. https://doi.org/10.1007/s40204-018-0095-0 (2018).

Article CAS PubMed PubMed Central Google Scholar

Zailani, M. A., Kamilah, H., Husaini, A., Awang Seruji, A. Z. R. & Sarbini, S. R. Starch modifications via physical treatments and the potential in improving resistant starch content. Starch Stärke 75, 2200146. https://doi.org/10.1002/star.202200146 (2023).

Article CAS Google Scholar

Masina, N. et al. A review of the chemical modification techniques of starch. Carbohydr. Polym. 157, 1226–1236. https://doi.org/10.1016/j.carbpol.2016.09.094 (2017).

Article CAS PubMed Google Scholar

Cai, Z. et al. The modification of properties of thermoplastic starch materials: Combining potato starch with natural rubber and epoxidized natural rubber. Mater. Today Commun. 26, 101912. https://doi.org/10.1016/j.mtcomm.2020.101912 (2021).

Article CAS Google Scholar

Karim, A. A., Sufha, E. H. & Zaidul, I. S. M. Dual modification of starch via partial enzymatic hydrolysis in the granular state and subsequent hydroxypropylation. J. Agric. Food Chem. 56, 10901–10907. https://doi.org/10.1021/jf8015442 (2008).

Article CAS PubMed Google Scholar

Onofre, F., Wang, Y. J. & Mauromoustakos, A. Effects of structure and modification on sustained release properties of starches. Carbohydr. Polym. 76, 541–547. https://doi.org/10.1016/j.carbpol.2008.11.016 (2009).

Article CAS Google Scholar

Mehboob, S., Ali, T. M., Alam, F. & Hasnain, A. Dual modification of native white sorghum (Sorghum bicolor) starch via acid hydrolysis and succinylation. LWT Food Sci. Technol. 64, 459–467. https://doi.org/10.1016/j.lwt.2015.05.012 (2015).

Article CAS Google Scholar

Otache, M. A., Duru, R. U., Achugasim, O. & Abayeh, O. J. Advances in the modification of starch via esterification for enhanced properties. J. Polym. Environ. 29, 1365–1379. https://doi.org/10.1007/s10924-020-02006-0 (2021).

Article CAS Google Scholar

Shoaib, A. G. M. et al. Starch-grafted-poly(acrylic acid)/Pterocladia capillacea-derived activated carbon composite for removal of methylene blue dye from water. Biomass Convers. Biorefinery https://doi.org/10.1007/s13399-022-03382-4 (2022).

Article Google Scholar

Chen, L. et al. Fabrication of starch-based high-performance adsorptive hydrogels using a novel effective pretreatment and adsorption for cationic methylene blue dye: Behavior and mechanism. Chem. Eng. J. 405, 126953. https://doi.org/10.1016/j.cej.2020.126953 (2021).

Article CAS Google Scholar

Ariaeenejad, S., Hosseini, E., Motamedi, E., Moosavi-Movahedi, A. A. & Salekdeh, G. H. Application of carboxymethyl cellulose-g-poly(acrylic acid-co-acrylamide) hydrogel sponges for improvement of efficiency, reusability and thermal stability of a recombinant xylanase. Chem. Eng. J. 375, 122022. https://doi.org/10.1016/j.cej.2019.122022 (2019).

Article CAS Google Scholar

He, G. et al. Preparation and properties of quaternary ammonium chitosan-g-poly(acrylic acid-co-acrylamide) superabsorbent hydrogels. React. Funct. Polym. 111, 14–21. https://doi.org/10.1016/j.reactfunctpolym.2016.12.001 (2017).

Article CAS Google Scholar

Namazi, H., Hasani, M. & Yadollahi, M. Antibacterial oxidized starch/ZnO nanocomposite hydrogel: Synthesis and evaluation of its swelling behaviours in various pHs and salt solutions. Int. J. Biol. Macromol. 126, 578–584. https://doi.org/10.1016/j.ijbiomac.2018.12.242 (2019).

Article CAS PubMed Google Scholar

Gupta, A. D., Rawat, K. P., Bhadauria, V. & Singh, H. Recent trends in the application of modified starch in the adsorption of heavy metals from water: A review. Carbohydr. Polym. 269, 117763. https://doi.org/10.1016/j.carbpol.2021.117763 (2021).

Article CAS PubMed Google Scholar

Abdolahi, G., Dargahi, M. & Ghasemzadeh, H. Synthesis of starch-g-poly(acrylic acid)/ZnSe quantum dot nanocomposite hydrogel, for effective dye adsorption and photocatalytic degradation: Thermodynamic and kinetic studies. Cellulose 27, 6467–6483. https://doi.org/10.1007/s10570-020-03198-3 (2020).

Article CAS Google Scholar

Foroughirad, S., Haddadi-Asl, V., Khosravi, A. & Salami-Kalajahi, M. Effect of porogenic solvent in synthesis of mesoporous and microporous molecularly imprinted polymer based on magnetic halloysite nanotubes. Mater. Today Commun. 26, 101780. https://doi.org/10.1016/j.mtcomm.2020.101780 (2021).

Article CAS Google Scholar

Cui, C. et al. Recent advances in the preparation, characterization, and food application of starch-based hydrogels. Carbohydr. Polym. 291, 119624. https://doi.org/10.1016/j.carbpol.2022.119624 (2022).

Article CAS PubMed Google Scholar

Dragan, E. S. Design and applications of interpenetrating polymer network hydrogels. A review. Chem. Eng. J. 243, 572–590. https://doi.org/10.1016/j.cej.2014.01.065 (2014).

Article CAS Google Scholar

Arafa, A. A. et al. Preparation and characterization of smart therapeutic pH-sensitive wound dressing from red cabbage extract and chitosan hydrogel. Int. J. Biol. Macromol. 182, 1820–1831. https://doi.org/10.1016/j.ijbiomac.2021.05.167 (2021).

Article CAS PubMed Google Scholar

Abdollahi, E., Khalafi-Nezhad, A., Mohammadi, A., Abdouss, M. & Salami-Kalajahi, M. Synthesis of new molecularly imprinted polymer via reversible addition fragmentation transfer polymerization as a drug delivery system. Polymer 143, 245–257. https://doi.org/10.1016/j.polymer.2018.03.058 (2018).

Article CAS Google Scholar

Khamizov, R. K. A pseudo-second order kinetic equation for sorption processes. Russ. J. Phys. Chem. A 94, 171–176. https://doi.org/10.1134/S0036024420010148 (2020).

Article CAS Google Scholar

Wu, F. C., Tseng, R. L. & Juang, R. S. Initial behavior of intraparticle diffusion model used in the description of adsorption kinetics. Chem. Eng. J. 153, 1–8. https://doi.org/10.1016/j.cej.2009.04.042 (2009).

Article CAS Google Scholar

Zheng, Y., Hua, S. & Wang, A. Adsorption behavior of Cu2+ from aqueous solutions onto starch-g-poly(acrylic acid)/sodium humate hydrogels. Desalination 263, 170–175. https://doi.org/10.1016/j.desal.2010.06.054 (2010).

Article CAS Google Scholar

Liu, Y. Some consideration on the Langmuir isotherm equation. Colloids Surf. A Physicochem. Eng. Aspects 274, 34–36. https://doi.org/10.1016/j.colsurfa.2005.08.029 (2006).

Article CAS Google Scholar

Benjelloun, M., Miyah, Y., AkdemirEvrendilek, G., Zerrouq, F. & Lairini, S. Recent advances in adsorption kinetic models: Their application to dye types. Arab. J. Chem. 14, 103031. https://doi.org/10.1016/j.arabjc.2021.103031 (2021).

Article CAS Google Scholar

Smail, O. & GökçeKocabay, O. Absorption and adsorption studies of polyacrylamide/sodium alginate hydrogels. Colloid Polym. Sci. 299, 783–796. https://doi.org/10.1007/s00396-020-04796-0 (2021).

Article CAS Google Scholar

Kowalski, G., Ptaszek, P. & Kuterasiński, L. Swelling of hydrogels based on carboxymethylated starch and poly(acrylic acid): Nonlinear rheological approach. Polymers 12, 2564. https://doi.org/10.3390/polym12112564 (2020).

Article CAS PubMed PubMed Central Google Scholar

Panahian, P., Salami-Kalajahi, M. & Hosseini, M. S. Synthesis of dual thermosensitive and pH-sensitive hollow nanospheres based on poly(acrylic acid-b-2-hydroxyethyl methacrylate) via an atom transfer reversible addition-fragmentation radical process. Ind. Eng. Chem. Res. 53, 8079–8086. https://doi.org/10.1021/ie500892b (2014).

Article CAS Google Scholar

El-saied, H. A. & El-Fawal, E. M. Green superabsorbent nanocomposite hydrogels for high-efficiency adsorption and photo-degradation/reduction of toxic pollutants from waste water. Polym. Test. 97, 107134. https://doi.org/10.1016/j.polymertesting.2021.107134 (2021).

Article CAS Google Scholar

Saberi, A., Sadeghi, M. & Alipour, E. Design of AgNPs-base starch/PEG-poly (acrylic acid) hydrogel for removal of mercury (II). J. Polym. Environ. 28, 906–917. https://doi.org/10.1007/s10924-020-01651-9 (2020).

Article CAS Google Scholar

Ma, D., Zhu, B., Cao, B., Wang, J. & Zhang, J. The microstructure and swelling properties of poly acrylic acid-acrylamide grafted starch hydrogels. J. Macromol. Sci. Part B 55, 1124–1133. https://doi.org/10.1080/00222348.2016.1242552 (2016).

Article ADS CAS Google Scholar

Czarnecka, E. & Nowaczyk, J. Synthesis and characterization superabsorbent polymers made of starch, acrylic acid, acrylamide, poly(vinyl alcohol), 2-hydroxyethyl methacrylate, 2-acrylamido-2-methylpropane sulfonic acid. Int. J. Mol. Sci. 22, 4325. https://doi.org/10.3390/ijms22094325 (2021).

Article CAS PubMed PubMed Central Google Scholar

Qiao, D. L. et al. Preparation of cassava starch-based superabsorbent polymer using a twin-roll mixer as reactor. Chin. J. Polym. Sci. 32, 1348–1356. https://doi.org/10.1007/s10118-014-1516-8 (2014).

Article CAS Google Scholar

Vudjung, C. & Saengsuwan, S. Synthesis and properties of biodegradable hydrogels based on cross-linked natural rubber and cassava starch. J. Elastomers Plast. 49, 574–594. https://doi.org/10.1177/0095244316676868 (2016).

Article CAS Google Scholar

Chen, J., Blevins, W. E., Park, H. & Park, K. Gastric retention properties of superporous hydrogel composites. J. Control. Release 64, 39–51. https://doi.org/10.1016/S0168-3659(99)00139-X (2000).

Article CAS PubMed Google Scholar

Czarnecka, E. & Nowaczyk, J. Semi-natural superabsorbents based on starch-g-poly(acrylic acid): Modification, synthesis and application. Polymers 12, 1794. https://doi.org/10.3390/polym12081794 (2020).

Article CAS PubMed PubMed Central Google Scholar

Chen, J. & Park, K. Synthesis and characterization of superporous hydrogel composites. J. Control. Release 65, 73–82. https://doi.org/10.1016/S0168-3659(99)00238-2 (2000).

Article CAS PubMed Google Scholar

Panahian, P., Salami-Kalajahi, M. & Hosseini, M. S. Synthesis of dual thermoresponsive and pH-sensitive hollow nanospheres by atom transfer radical polymerization. J. Polym. Res. 21(6), 455. https://doi.org/10.1007/s10965-014-0455-y (2014).

Article CAS Google Scholar

Sadeghi, M. Synthesis of starch-g-poly(acrylic acid-co-2-hydroxy ethyl methacrylate) as a potential pH-sensitive hydrogel-based drug delivery system. Turk. J. Chem. 35, 723–733. https://doi.org/10.3906/kim-1103-27 (2011).

Article CAS Google Scholar

Chang, A. pH-sensitive starch-g-poly(acrylic acid)/sodium alginate hydrogels for controlled release of diclofenac sodium. Iran. Polym. J. 24, 161–169. https://doi.org/10.1007/s13726-015-0311-x (2015).

Article CAS Google Scholar

Lima-Tenório, M. K. et al. Water transport properties through starch-based hydrogel nanocomposites responding to both pH and a remote magnetic field. Chem. Eng. J. 259, 620–629. https://doi.org/10.1016/j.cej.2014.08.045 (2015).

Article CAS Google Scholar

Mohammadi, R., Saboury, A., Javanbakht, S., Foroutan, R. & Shaabani, A. Carboxymethylcellulose/polyacrylic acid/starch-modified Fe3O4 interpenetrating magnetic nanocomposite hydrogel beads as pH-sensitive carrier for oral anticancer drug delivery system. Eur. Polym. J. 153, 110500. https://doi.org/10.1016/j.eurpolymj.2021.110500 (2021).

Article CAS Google Scholar

Zhang, Y., Gao, P., Zhao, L. & Chen, Y. Preparation and swelling properties of a starch-g-poly(acrylic acid)/organo-mordenite hydrogel composite. Front. Chem. Sci. Eng. 10, 147–161. https://doi.org/10.1007/s11705-015-1546-y (2016).

Article CAS Google Scholar

Arayaphan, J., Maijan, P., Boonsuk, P. & Chantarak, S. Synthesis of photodegradable cassava starch-based double network hydrogel with high mechanical stability for effective removal of methylene blue. Int. J. Biol. Macromol. 168, 875–886. https://doi.org/10.1016/j.ijbiomac.2020.11.166 (2021).

Article CAS PubMed Google Scholar

Wang, L., Zhang, J. & Wang, A. Removal of methylene blue from aqueous solution using chitosan-g-poly(acrylic acid)/montmorillonite superadsorbent nanocomposite. Colloids Surf. A 322, 47–53. https://doi.org/10.1016/j.colsurfa.2008.02.019 (2008).

Article ADS CAS Google Scholar

Ighalo, J. O., Iwuozor, K. O., Igwegbe, C. A. & Adeniyi, A. G. Verification of pore size effect on aqueous-phase adsorption kinetics: A case study of methylene blue. Colloids Surf. A Physicochem. Eng. Aspects 626, 127119. https://doi.org/10.1016/j.colsurfa.2021.127119 (2021).

Article CAS Google Scholar

Gayathri, K. & Palanisamy, N. Methylene blue adsorption onto an eco-friendly modified polyacrylamide/graphite composites: Investigation of kinetics, equilibrium, and thermodynamic studies. Sep. Sci. Technol. 55, 266–277. https://doi.org/10.1080/01496395.2019.1577261 (2020).

Article CAS Google Scholar

Doğan, M., Abak, H. & Alkan, M. Adsorption of methylene blue onto hazelnut shell: Kinetics, mechanism and activation parameters. J. Hazard. Mater. 164, 172–181. https://doi.org/10.1016/j.jhazmat.2008.07.155 (2009).

Article CAS PubMed Google Scholar

Nikravan, G., Haddadi-Asl, V. & Salami-Kalajahi, M. Synthesis of dual temperature- and pH-responsive yolk-shell nanoparticles by conventional etching and new deswelling approaches: DOX release behavior. Colloids Surf. B 165, 1–8. https://doi.org/10.1016/j.colsurfb.2018.02.010 (2018).

Article CAS Google Scholar

Van Assche, T. R. C., Baron, G. V. & Denayer, J. F. V. An explicit multicomponent adsorption isotherm model: Accounting for the size-effect for components with Langmuir adsorption behavior. Adsorption 24, 517–530. https://doi.org/10.1007/s10450-018-9962-1 (2018).

Article CAS Google Scholar

Bello, K., Sarojini, B. K., Narayana, B., Rao, A. & Byrappa, K. A study on adsorption behavior of newly synthesized banana pseudo-stem derived superabsorbent hydrogels for cationic and anionic dye removal from effluents. Carbohydr. Polym. 181, 605–615. https://doi.org/10.1016/j.carbpol.2017.11.106 (2018).

Article CAS PubMed Google Scholar

Foo, K. Y. & Hameed, B. H. Insights into the modeling of adsorption isotherm systems. Chem. Eng. J. 156, 2–10. https://doi.org/10.1016/j.cej.2009.09.013 (2010).

Article CAS Google Scholar

Rossetto, R., Maciel, G. M., Bortolini, D. G., Ribeiro, V. R. & Haminiuk, C. W. I. Acai pulp and seeds as emerging sources of phenolic compounds for enrichment of residual yeasts (Saccharomyces cerevisiae) through biosorption process. LWT 128, 109447. https://doi.org/10.1016/j.lwt.2020.109447 (2020).

Article CAS Google Scholar

Eldin, M. S. et al. Carboxylated alginate hydrogel beads for methylene blue removal: Formulation, kinetic and isothermal studies. Desalin. Water Treat. 168, 308–323. https://doi.org/10.5004/dwt.2019.24628 (2019).

Article CAS Google Scholar

Hu, X.-S., Liang, R. & Sun, G. Super-adsorbent hydrogel for removal of methylene blue dye from aqueous solution. J. Mater. Chem. A 6, 17612–17624. https://doi.org/10.1039/C8TA04722G (2018).

Article CAS Google Scholar

Download references

Department of Polymer Engineering and Color Technology, Amirkabir University of Technology, Tehran, Iran

Fatemeh Mohammadzadeh & Vahid Haddadi-Asl

Faculty of Polymer Engineering, Sahand University of Technology, P.O. Box 51335-1996, Tabriz, Iran

Marzieh Golshan & Mehdi Salami-Kalajahi

Institute of Polymeric Materials, Sahand University of Technology, P.O. Box 51335-1996, Tabriz, Iran

Marzieh Golshan & Mehdi Salami-Kalajahi

You can also search for this author in PubMed Google Scholar

F.M.: methodology, formal analysis, investigation, writing—original draft, visualization. M.G.: methodology, formal analysis, investigation, visualization. V.H-A.: validation, resources, writing—review and editing, supervision. M.S-K.: conceptualization, validation, resources, data curation, writing—review and editing, supervision, project administration, funding acquisition.

Correspondence to Vahid Haddadi-Asl or Mehdi Salami-Kalajahi.

The authors declare no competing interests.

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.

Reprints and Permissions

Mohammadzadeh, F., Golshan, M., Haddadi-Asl, V. et al. Adsorption kinetics of methylene blue from wastewater using pH-sensitive starch-based hydrogels. Sci Rep 13, 11900 (2023). https://doi.org/10.1038/s41598-023-39241-z

Download citation

Received: 08 June 2023

Accepted: 21 July 2023

Published: 24 July 2023

DOI: https://doi.org/10.1038/s41598-023-39241-z

Anyone you share the following link with will be able to read this content:

Sorry, a shareable link is not currently available for this article.

Provided by the Springer Nature SharedIt content-sharing initiative

By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.

'Barbie' success boosts rivals in battered toy industry: 'Pink tide is lifting in toyland'

What to Use Instead of Soda Ash for Tie Dye

News

Adsorption kinetics of methylene blue from wastewater using pH