DOI:
10.1039/D5TC01581B
(Paper)
J. Mater. Chem. C, 2025, Advance Article
Biodegradable CMC/Zn/Ca/Cu cross-linked novel superabsorbent hydrogel bead for plant pathogen prevention and agricultural applications
Received
17th April 2025
, Accepted 1st August 2025
First published on 4th August 2025
Abstract
Multi-nutrient-loaded biodegradable and biocompatible carboxymethyl cellulose-based zinc, calcium, and copper cross-linked hydrogel bead (CMC@CC) was prepared through an ionic cross-linking method. Further, nitrate was loaded in CMC@CC to obtain NCMC@CC. Under optimized conditions, CMC@CC showed an equilibrium swelling ratio of ∼915% in distilled water. The swelling kinetics of the hydrogel bead in water under optimized conditions followed both Fickian diffusion and second-order kinetic models. NCMC@CC exhibited a slow-release profile of nitrate in water and was better fitted by the Korsmeyer–Peppas model, and the release of nitrate was controlled by diffusion mechanism. The functional efficacy of the NCMC@CC nanocomposite beads was investigated by studying the growth pattern of tomato plants (Solanum lycopersicum L.) in soil. The application of NCMC@CC showed significant growth compared with control treatment. In vitro antibacterial study of the prepared hydrogel bead against Ralstonia solanacearum F1C1, a plant pathogen responsible for wilt disease in tomato, revealed that the prepared hydrogel bead possessed great bactericidal efficacy. These dual functional hydrogel bead could simultaneously reduce the application of pesticides and fertilizers for plant growth, thus promoting sustainability.
1. Introduction
The issues associated with food production are expanding alarmingly with the increasing world population and urbanization. In response to global food demands, farmers are applying huge amounts of fertilizers to maximize the crop yield.1,2 The soil continues to be polluted by petrochemical derivatives, crude oil, fertilizers, heavy metals and polycyclic aromatic hydrocarbons.3,4 Nitrogen (N) fertilizers are rampantly used in agriculture for maximizing the yield.5 Only 20–30% of N fertilizers are effectively used by plants and the rest leach, potentially polluting the farmland soil and groundwater.6 Soil pollution has seriously endangered biodiversity and human health. Increasing the concentration of fertilizers in agricultural wastewater has led to widespread eutrophication in aquatic environments.7 After several decades of research, although organic and inorganic substances including zeolite, mesoporous hollow silica, and montmorillonite have been introduced to regulate the release of conventional chemical fertilizers, their extraction is a costly process.8 Therefore, there is an urgent need to find a cost-effective method for the replacement of traditional fertilizers.
Recently, slow-release fertilizer (SRF) systems made from nanocomposite hydrogels have attracted a lot of attention for their advantage of dosing and reduced poisoning.9,10 Hydrogels are hydrophilic polymer materials that are cross-linked to form insoluble matrixes at physiological temperature, pressure, ionic strength and pH.11,12 The hydrophilicity arises due to the presence of –NH2, –COOH, –OH and –CONH2 groups and the combined effect of capillary and osmotic pressures.13 Hydrogels can retain biological fluids or water and swell several times their dry volumes owing to their cross-linked network structure. The structure, chemistry and functionality of hydrogel systems can be manipulated, making them potential candidates in various applications including drug delivery, shape morphing, tissue engineering and agriculture and as soft actuators and artificial muscles.14,15 Their aqueous environment permits the transportation of substances such as drugs and nutrients throughout its surrounding medium; however, their properties are reliant on the polymer hydrophilicity, polymer iconicity, type of recognition entity and cross-linking density.16,17
Controllable methods for preparing hydrogels include radiation cross-linking, chemical cross-linking and physical cross-linking.18 The majority of hydrogel composites have low degradability.10 However, there is an emerging demand and expanding interest in the synthesis of cellulose-based hydrogels for soil water retention and as a nutrient release agent. One particular starting material that has been comprehensively studied for agricultural application is carboxymethyl cellulose (CMC). The CMC-based hydrogel can be extensively used for wound dressing, drug delivery, protein purification, crystallization of minerals, distillation and heavy metal capturing. CMC with many hydroxyl and carboxylic groups is considered a green, natural, inexpensive, nontoxic, biodegradable and biocompatible material.19,20 Embedding inorganic components with a hydrogel matrix is an excellent strategy to overcome the inherent limitations of cellulose-based hydrogels.21 The high absorption ability, low cost, biodegradability, biocompatibility and non-toxicity of CMC make it an ideal cellulose derivative for preparing hydrogels.22,23
Macronutrients and micronutrients are essential for plant growth and metabolism. Macronutrients such as nitrogen (N) and calcium (Ca) and micronutrients such as zinc (Zn) and copper (Cu) play a pivotal role in plant physiology.24 N is known as a vital nutrient for crops to promote a healthier root system and to improve plant growth.25 Ca participates in stimulus-response coupling and activates proteins such as phosphatases or phospholipases and kinases.24,26 As essential plant nutrients, Zn and Cu participate in several physiological processes.27,28 Micronutrients participate in plant metabolism, nitrogen transformation and protein synthesis and contribute to the development and structure formation of tissue. Their deficiency negatively affects plant growth.29 The incidence of micronutrient deficiency in crops will be minimized by applying multi-nutrient precise fertilization in the vicinity of plants. The majority of micronutrients are co-granulated or co-delivered with a macronutrient fertilizer. Despite mounting evidence on the importance of hydrogel nanocomposite as an SRF system and the composites that might be a way to sustain plant growth, very limited information is available. On the other hand, plant pathogen is the major cause of food shortage. Tomato (Solanum lycopersicum L.) is one of the most popular crops and the second cultivated horticultural crop in the world. One-third of the global crops are lost due to insect injuries and pathogenic diseases.30 Fungal infection of tomato can cause necrosis in the stem and later complete defoliation, which ultimately leads to death of the plant, accounting for up to 80% loss of tomato crop.31 Bacterial wilt caused by Ralstonia solanacearum is a serious soil-borne disease, and this bacterium causes wilt by infecting many plants, including tomato, through the roots and colonizing the stem of vascular tissue.32 Management of tomato production against this pathogen is crucial to maximize the crop's yield. Different approaches are developed to control this disease via the application of chemicals, soil disinfectants, antibiotics, organic amendments, and bacterial antagonists and the use of resistant varieties.33 However, the hazardous effects of agrochemicals on the environment and the frequent breakdown of resistant varieties needed an alternative and sustainable disease management approach.33,34 Bactericidal hydrogel nanocomposites could be exploited for such bacterial diseases.
Inspired by this background, we herein developed a facile strategy for encapsulation of plant growth ingredients in a hydrogel matrix made from carboxymethyl polymer via an ionic cross-linking mechanism that does not require any synthetic polymeric material. Herein, we report the synthesis of a multi-nutrient hydrogel by intermolecular cross-linking of CMC with ZnO and calcium chloride, followed by the addition of copper sulfate. The CMC/ZnO/Ca cross-linked beads (CMC@C) are soluble in water; therefore, they are further coated with copper by dipping the CMC@C beads in a copper sulfate solution. These beads are further loaded with a nitrate solution for slow N delivery. All the beads are thoroughly characterized by FTIR spectroscopy, SEM-EDX, XPS, XRD and rheological analysis. The performance of increased water retention capacity and synchronously slow release of nitrate has been realized. The major parameters that impact the swelling ratio of hydrogels were systematically evaluated. After degradation, the composite eventually releases plant nutrients such as Zn, Ca and Cu in the plant's available form. The nutrient delivery profile and effects of these hydrogels on soil and on the growth pattern of tomato plants (Solanum lycopersicum L.) were studied. Moreover, the in vitro antibacterial study was conducted to screen the antibacterial activity of the prepared hydrogel bead against tomato bacterial wilt pathogen Ralstonia solanacearum F1C1. These dual action beads could deliver nutrients and also act as bactericides for pathogen infection prevention in plants, thus promoting sustainability.
2. Experimental section
2.1 Materials
Sodium carboxymethyl cellulose (high viscosity) having the molecular formula [C6H7O2(OH)x(OCH2COONa)y]n (n = approx. 500) was purchased from TCI (Tokyo, Japan). Zinc chloride hexahydrate (ZnCl2·6H2O, extrapure), sodium nitroprusside (extrapure, 98%) and dipotassium hydrogen phosphate (Na2HPO4, extrapure) were obtained from Finar (Ahmedabad, Gujrat, India). Potassium chloride and calcium chloride dihydrate (extrapure) were obtained from Loba Chemie (Mumbai, Maharashtra, India). Sodium chloride, potassium nitrate and copper sulfate pentahydrate were obtained from Rankem (India). N-(1-Napthyl)ethylenediamine dihydrochloride (NEDA; extrapure; AR, ACS, 98%), sodium hypochlorite solution (4–7% Cl), copper(II) sulfate pentahydrate (pure, 98%), sodium hydroxide (pure, 98%), and buffer capsules of pH 4, 7 and 9.2 were obtained from Sisco Research Laboratories Pvt. Ltd (Mumbai, India). De-ionized water was used as a solvent for fabricating the hydrogels.
2.2 Preparation of hydrogels
Hydrogel bead were prepared by a simple ionic cross-linking method, as briefly illustrated below. Initially, 4% CMC was added to 40 mL distilled water at room temperature and stirred until a viscous medium was obtained. Then, 10 mL zinc chloride solutions of different concentrations (shown in Table 1) were added slowly into the CMC solution. After stirring for 5 hours, solid sodium hydroxide (0.736 g) was added to the above-mentioned solution and stirred for another 4 hours. For the formation of homogeneous uniform spherical beads, the cross-linked CMC solution was drop-wise added into a calcium chloride solution using a syringe pump (at a rate of 100 mL per hour); meanwhile, the calcium chloride solution was stirred at a rate of 200 rpm. CMC/ZnO/Ca hydrogel bead (CMC@C) were allowed to stand for 1 hour in the calcium chloride solution to achieve the maximum cross-linking. The white color circular beads formed were filtered and washed with a suitable amount of ethanol to remove the unreacted chemical. CMC@C beads are not suitable for application as the cross-linked network breaks when it comes in contact with water. To overcome this inherent limitation, CMC@C was further soaked in a copper sulfate (2.5 g 50 mL−1) solution for 12 hours. The calcium and copper cross-linked hydrogel bead (CMC@CC) were filtered and washed several times with distilled water. Finally, beads were dried for 6 hours in a vacuum desiccator and then oven-dried to carry out further analysis. Six different types of hydrogel bead were prepared, and their composition is shown in Table 1. Table 1 depicts the minimum concentrations of calcium and copper salts that are necessary for the formation of well-developed hydrogel bead. By lowering the concentration of both the reagents (Ca, and Cu) as mentioned in Table 1, well-developed hydrogel bead were not formed. Under optimized conditions, i.e. for the MH-4 sample (named as CMC@CC), the size of the hydrogel bead was found to be 0.3 cm in swollen form, as displayed in Fig. S1(b). From the digital images, it can be seen that the hydrogel bead have smooth surfaces in a swollen state, but after drying, the beads turn rough and the size is reduced to 0.2 cm (see Fig. S1(c)).
Table 1 Weight ratio of components in CMC/zinc chloride/calcium chloride/copper sulfate nanocomposite hydrogel bead
Sample code |
CMC (g/50 mL) |
Zinc chloride (g/10 mL) |
Zinc chloride (M) (10 mL) |
Calcium chloride (g/50 mL) |
Copper sulfate (g/50 mL) |
MH-1 |
2 |
0.03 |
0.022 |
5 |
2.5 |
MH-2 |
2 |
0.06 |
0.044 |
5 |
2.5 |
MH-3 |
2 |
0.09 |
0.066 |
5 |
2.5 |
MH-4 |
2 |
0.3 |
0.220 |
5 |
2.5 |
MH-5 |
2 |
0.45 |
0.330 |
5 |
2.5 |
MH-6 |
2 |
0.6 |
0.440 |
5 |
2.5 |
2.3 Characterization
The morphological analysis of hydrogel was carried out using a scanning electron microscope (Jeol 6390LA/OXFORD XMX N). The images were observed at different magnifications at an accelerating voltage of 15 kV. The elemental analysis of hydrogels was performed by EDX. The FTIR spectra of the samples were studied using an FTIR spectrometer (Agilent Model No. Cary 630, United States; SL. No. MY20192018), within the range of 400–4000 cm−1. XRD spectra were obtained using a Bruker D8 Advance instrument in the 2θ range of 2°–50° at a scan rate of 2° min−1. The thermal stability of hydrogel bead was investigated by thermogravimetric analysis (TGA) and differential scanning calorimetry (DSC) (Make: Hitachi, Model: NEXTA STA300) at a heating rate of 10 °C min−1 in a nitrogen atmosphere. To analyze the surface chemistry of materials, X-ray photoelectron spectroscopy (XPS) was performed using an Auger electron spectroscopy module (Model: PHI5000 Versa Prob II, FEI Inc.). Frequency sweep measurements were performed in a measuring mode at a frequencies ranging from 0.1 to 10 Hz, to determine the values of storage modulus (G′) and loss modulus (G′′). During the frequency sweep test, a rheometer with a parallel stainless-steel plate was applied to measure the value of the loss tangent.
2.4 Determination of the swelling ratio (SR)
The tea bag method is the most conventional method for measuring the swelling ratio of the hydrogel. A definite amount of hydrogel bead was placed into a tea bag, and the bag was immersed entirely in an excessive amount of swelling medium and allowed to swell until it reached an equilibrium state. Swelling data were collected at regular periods under ambient conditions. To remove surface water, the tea bag was hung for 15 minutes, followed by soft pressing the tea bag sample between the folds of filter paper. The same procedure was also analyzed for an empty bag. The swelling ratio of the hydrogel was measured using eqn (1): |
 | (1) |
Wt is the weight of the tea bag after time t, Wd is the dry weight of hydrogel bead, and Wa is the weight of the tea bag. The sensitivity of the hydrogel bead was measured in distilled water, saline medium and also in different pH media.
2.5 Swelling kinetics
To study the effect of the composition of cross-linkers on the kinetics of water uptake of hydrogels, the swelling data were fitted into two kinetic models, namely, Fickian diffusion (eqn (2)) and second-order kinetic (eqn (3)) models, to analyze the experimental data. The Fickian diffusion equation is as follows: |
 | (2) |
where Qt is the degree of swelling ratio at time t, Qeq is the equilibrium or maximum swelling ratio of the hydrogel, and kp is the swelling rate constant. The second-order kinetic model is written as follows: |
 | (3) |
where Seq is the theoretical equilibrium swelling, the relationship Kis = KsSeq2 is the initial swelling rate constant and Ks is the swelling rate constant.35
2.6 Study the loading and release of fertilizers
Potassium nitrate was considered as a model fertilizer and loaded in the prepared hydrogel bead via the sorption mechanism. This was performed by immersing pre-weighed dry CMC@CC samples in a 0.1 M potassium nitrate solution and allowed to attain maximum swelling. The swollen samples were subsequently dried at 30 °C and stored for further analysis. The fertilizer-loaded sample was named NCMC@CC. The loading efficiency (LE) of nitrate was calculated using eqn (4): |
 | (4) |
where W0 is the initial amount of nitrate and W1 is the amount of nitrate left in the solution.
The fertilizer release profile was measured under both water and soil conditions. To determine the fertilizer release profile, 2 g hydrogel composite beads were placed into a 250 mL volumetric flask containing distilled water. After a definite interval of time, 1 mL aliquots of corresponding media solutions were withdrawn, and 1 mL of the corresponding fresh sample was added to maintain the constant volume. The absorbance of the supernatant was read using a UV-visible spectrophotometer at 369 nm. The cumulative release rate of nitrate (Cr) was calculated using eqn (5):
|
 | (5) |
where
n is the time of aliquot collection and 0 <
i <
n.
Cn is the concentration of fertilizer in the release medium after the removal of the nth sample.
V0 is the total volume of release medium, whereas
Ve is the volume of solution collected at time
i, and
M0 is the mass of fertilizer in the hydrogel bead. The release kinetics of the fertilizer were also measured, and the kinetics equations are shown in Section S2.
2.7 Pot experiments and in vitro screening of antibacterial activities
Tomato (Solanum lycopersicum L.) was selected as a model plant to evaluate the effect of hydrogels on its growth. The seeds of the tomato were selected to be nearly of equal size. The seeds were sterilized with a 10% NaClO solution. To determine the effectiveness of the hydrogel, tomato seeds were allowed to grow under the following treatments: control (only soil); CMC@CC-soil and NCMC@CC-soil. Equal amounts of tomato seeds were placed in plastic boxes containing a definite amount of soil and the pot studies were conducted under normal laboratory conditions. Three replicates were carried out for each treatment. All the treatments were given equal amounts of tap water daily to ensure an adequate water supply. After 9 days of plantation, the plants were collected. The growth of plants was measured in terms of shoot and root length, as well as dry and fresh weight of biomass.
For the antibacterial studies, pre-identified preserved bacterial culture of R. solanacearum was procured from Assam Agricultural University, Jorhat, Assam, India. The antagonistic activity of the prepared hydrogel bead against R. solanacearum was evaluated by an agar diffusion method. The optimized hydrogel bead, i.e., CMC@CC, were tested for in vitro study for their ability to inhibit the growth of R. solanacearum. For this purpose, an initially fresh pure culture of the above-mentioned strain was inoculated on an agar plate containing hydrogel bead. A control sample was also prepared without the addition of hydrogel bead. The antibacterial activity was evaluated by measuring the inhibition zone observed around each of the disks after 48 hours of incubation. This was done three times for both the control sample and the hydrogel bead.
2.8 Statistical analysis of data
The plant study data were analyzed using one-way analysis of variance (ANOVA) followed by pairwise comparison using the least significant difference test (LSD). The LSD values were calculated at the percentage probability levels (p = 0.05) to determine the significance of differences between any two treatment averages. The significance of treatment variation vs. error variance was measured using the variance ratio.
3. Results and discussion
3.1 FTIR analysis
FTIR spectroscopy was used to relate the possible interactions in the hydrogel molecules. The FTIR spectra of pure CMC and the composite at each step of preparation are presented in Fig. 1. Major peaks are magnified in Fig. 1(b) and (c). A wide peak observed in all the samples at around (3000–3500) cm−1 was due to the –OH stretching frequency, and a band at (1614–1625) cm−1 was attributed to the C
O stretching frequency of the CMC molecule. After the addition of zinc chloride, both –OH and C
O bands of CMC/Zn suspension (CMC@Z) were shifted to a lower wavelength with a decrease in transmittance that that of pure CMC, indicating a possible interaction of hydroxyl and carbonyl groups with Zn2+ ions. The –OH stretching frequency in CMC@Z is extremely broad, indicating the chance of huge intermolecular hydrogen bonding of CMC with Zn2+ ions. Moreover, after the addition of sodium hydroxide, this –OH stretching vibration again shifted to higher transmittance and became less broad than that of CMC@Z.
 |
| Fig. 1 FTIR spectra of hydrogels at each step of preparation (CMC@Z → CMC + ZnCl2; CMC@B → CMC + ZnCl2 + NaOH) at different wavenumbers ranging within (a) 400–4000 cm−1, (b) 2500–4500 cm−1, and (c) 400–2000 cm−1. (d) FTIR spectra of final hydrogel bead. | |
Sodium hydroxide converts Zn2+ into ZnO nanoparticles, which was ascribed by the vibrational stretching frequency at 599 cm−1, and due to this some intermolecular bonding was also destroyed. Furthermore, Fig. 1(d) depicts the FTIR spectra of CMC@CC, i.e., after cross-linking with calcium chloride and copper sulphate. Here, the characteristics vibration bands at 530 cm−1 and 1420 cm−1 were related to the stretching vibration of nano ZnO and the –CH2 scissoring vibration of CMC molecules, respectively. Furthermore, it is noted that after the addition of calcium chloride and copper sulphate, both –OH and C
O stretching vibrations again shifted to 3400 cm−1 and 1625 cm−1, respectively, suggesting the establishment of new non-covalent interactions with calcium and copper ions. The appearance of multiple peaks instead of the usual one broad band for asymmetric single stretching is indicative of different hydrogen bonding environments resulting from the interactions of calcium and copper ions with hydroxyl groups. The change in the FTIR spectra of CMC@CC proves that both calcium and copper can be successfully entrapped into the hydrogel network system. The FTIR spectra of KNO3 and NCMC@CC are shown in (see Fig. S2). The peaks at 830 cm−1 and 1380 cm−1 correspond to the angular anti-symmetric deformation of O–N–O and the anti-symmetric stretching mode of free nitrate ion, respectively.36 These peaks also appeared for NCMC@CC, which, in turn, confirmed the successful loading of nitrate in the hydrogel composite.
3.2 Morphological and rheology analysis
SEM measurements were carried out to analyze the surface morphology of the prepared hydrogel bead in both swollen and dry forms. The outer surface and cross-sectional morphology of CMC@C are portrayed in Fig. S3 and S4, respectively. The outer layer is associated with a rough and porous structure, which may be the result of the formation of a cross-linked structure with calcium ions. Fig. S3(d) and S4(d) represent the EDX spectra of the outer surface and the cross-section of CMC@C, which confirm the presence of all the characteristic elements. The cross-sectional morphology of CMC@C beads shows a distinct morphology compared with the outer surface. Fig. 2(a)–(c) and (g)–(i) show the top view of CMC@CC in both swollen and dry forms, respectively, at different magnifications. CMC@CC possesses a smooth surface in a swollen state and a rough surface with large wrinkles in a dry state, as shown in Fig. 2(a) and (g), respectively. Fig. 2(d)–(f) and (j)–(l) show the cross-sectional images of CMC@CC in both swollen and dry forms, respectively, at different magnifications. It can be seen that the cross-sectional images of CMC@CC show different morphologies and pore structures as compared to the outer surface. The EDX spectra of CMC@CC in both swollen and dry forms are shown in Fig. S5. The functionalized porous 3D network with nano ZnO will provide more adsorption sites in the hydrogel, which may be suitable for the immigration and emigration of fertilizers and hence enhance its efficiency towards sustainable agricultural applications. Similar in situ formation of nano ZnO in carboxymethyl cellulose-based hydrogel composites has also been reported by other researchers.37,38 Moreover, rheological analysis was also performed for all the hydrogel bead, as shown in Fig. S6, and the rheological behavior is explained in (see Section S6).
 |
| Fig. 2 SEM micrographs of CMC@CC at different magnifications: (a), (b) and (c) swollen form and (g), (h) and (i) dry form. Cross-sectional SEM micrographs of CMC@CC at different magnifications: (d), (e), (f) swollen form and (j), (k) and (l) dry form. | |
3.3 Thermal analysis
To gain some knowledge about the thermal properties of nanocomposites, the thermal degradation behavior was examined and compared with the pure CMC. Thermogravimetry analysis of CMC@CC and NCMC@CC is exhibited in Fig. 3(a) and (b), respectively. The TGA, DTA and DSC thermograms of pure CMC are shown in Fig. S7.
 |
| Fig. 3 TGA and DSC thermograms of (a) CMC@CC and (b) NCMC@CC. (c) XRD spectra of CMC@CC and NCMC@CC. | |
The pure CMC sample experienced two stages of weight loss: the major decomposition started at (222–600) °C with a weight loss of ∼49% due to the inorganic moiety,39 and a minor decomposition (14.5%) at <220 °C. Meanwhile, the degradation process of the hydrogel is divided into three distinct steps. The first-stage degradation occurred for both the samples at <150 °C, with ∼14.46% and ∼12.96% of overall weight loss for CMC@CC and NCMC@CC, respectively. This may be attributed to the elimination of absorbed water and the decomposition of low-molecular weight compounds. At this stage, the decomposition of side groups of polymers or copolymers and the destruction of cross-linking or non-cross-linking sites occur. The third stage degradation occurred at (281–600) °C with ∼20.46% weight loss for CMC@CC and at (265–600) °C with ∼19.80% weight loss for NCMC@CC. At 600 °C, ∼50.10% and ∼47.715% of CMC@CC and NCMC@CC are left, indicating that only half of the hydrogel was degraded at 600 °C. The increasing trend of decomposition temperature states that the thermal stability of CMC@CC is better than NCMC@CC. The exothermic peak appeared at ∼115 °C for CMC@CC, which is characteristic of the hydrogel. Moreover, this peak has shifted to ∼127 °C for NCMC@CC due to the formation of some non-covalent interactions between potassium nitrate and hydrogel bead. Furthermore, the DTA curves for both CMC@CC and NCMC@CC are shown in Fig. S8. Here, the obtained peaks demonstrated the characteristics of the hydrogel.
3.4 XRD analysis
To confirm the in situ formation of ZnO nanoparticles within the hydrogel matrix, XRD analysis was performed. The XRD pattern of pure CMC is shown in (see Fig. S9). CMC displays a large band at 22.6° corresponding to the (200) plane, indicating a relatively ordered structure characterized by the crystalline form of cellulose.40 The XRD pattern of CMC@CC and NCMC@CC within the 2θ range of 2–80° is shown in Fig. 3(c). The (200) plane corresponds to CMC's remaining intake in both the hydrogels, and the peaks become sharper in hydrogel bead, resulting in higher perfection of the crystal lattice in this plane than in the CMC sample. We assign the peaks of CMC@CC at 2θ = 31°, 34°, 37°, 47°, 56°, 68° and 76° to the (100), (002), (101), (102), (110), (112) and (202) crystallographic planes of ZnO, indicating that the nano ZnO was formed in the polymer matrix. The characteristic peaks of nano ZnO in NCMC@CC are slightly shifted as compared to CMC@CC. This may arise due to the generation of some non-covalent interactions between CMC@CC with potassium nitrate. Moreover, the additional peaks that appeared at 2θ of 39.18, 47.17 and 32 could be assigned to the (200), (202) and (110) diffraction of CuO nanoparticles, respectively. During the loading of Cu2+ ions in the hydrogel matrix, some copper ions are converted into the CuO form.41,42
3.5 XPS analysis
XPS measurements have been used to investigate the chemical state and to analyze the interactions between metal ions within the hydrogel matrix and with the fertilizer. The full-scan XPS survey of CMC@CC and NCMC@CC is shown in (see Fig. S10), which reveals the presence of C, O, Zn, Ca and Cu in the hydrogel matrix. Fig. 4(a) and (c) display the high-resolution survey scan of CMC@CC and NCMC@CC for C 1s, and it is deconvoluted into four peaks at 283.38/284.6 eV, 289.19/289.10, 285.76/285.84 and 287.79/287.80 corresponding to C–C, –O–C
O, C–OH and C
O, respectively. Fig. 4(b), (d) and (e) depict the high-resolution XPS spectra for Ca 2p, Zn 2p and Cu 2p, respectively. The peaks that appeared at 346.5 eV and 350.07 eV are in perfect agreement with the characteristics of Ca 2p1/2 and Ca 2p3/2, respectively.43 Here, ZnO nanoparticles in the hydrogel matrix display Zn 2p peak positions at different binding energy values as compared to pure ZnO. For Zn 2p, two peaks appeared at 1021.04 and 1044.1 corresponding to Zn 2p3/2 and Zn 2p1/2, respectively, whereas in pure ZnO, they appeared at 1021.48 eV and 1044.58 eV for Zn 2p3/2 and Zn p1/2, respectively.44,45 The characteristic peaks at 932.7 eV and 952.5 eV were attributed to Cu 2p3/2 and Cu 2p1/2, respectively.46 The CuO peak was observed at 942.5 eV, and this peak is slightly shifted due to the interaction with the polymer matrix. A similar type of spectrum for CuO was also reported by Zhang et al.47
 |
| Fig. 4 High-resolution XPS spectra of (a) C 1(s) of CMC@CC, (c) C 1(s) of NCMC@CC, (b), (d) and (e) both CMC@CC and NCMC@CC at different binding energies. | |
3.6 Plausible mechanism of the formation of hydrogel bead
The formation of homogeneous circular hydrogel bead can be attributed to strong interaction via hydrogen bonds between carboxyl and hydroxyl groups with cross-linkers, and the predicted mechanism is schematically depicted in Fig. 5. The figure represents the plausible interactions based on characterization techniques and the available literature. The beads forming cross-linking agent calcium chloride and copper sulphate were assumed to act by complexation of the carboxylate anion of CMC by its divalent calcium and copper ions. When CMC/Zn/NaOH suspension (CMC@B) came into contact with calcium chloride, the cations immediately interacted with the anionic polyelectrolyte and formed circular beads on the drop surface. From the FTIR spectrum (Fig. 1), it is seen that after the addition of ZnCl2, both –OH and C
O, stretching frequencies have shifted, resulting in the formation of hydrogen bonding interactions of Zn2+ with –OH and C
O groups, as shown in Fig. 5(ii). Moreover, after the addition of NaOH, both these stretching frequencies shifted, as at lower temperatures, the –OH ions break the hydrogen bonding interactions in cellulose molecules, and therefore, some interactions are broken.48 The formation of ZnO was confirmed by FTIR spectroscopy and XRD analysis. It is assumed that the in situ formation of ZnO will push the hydrogel chain towards the bead formation. A similar type of interaction of CMC or alginate with Zn2+ was reported by Priyadarshi et al.,49 Kumar et al.,50 and Ekanayake et al.51 When CMC@C beads are dried and allowed to be studied in the water; then the beads are degraded. Therefore, after cross-linking with calcium, the beads are washed with ethanol; as water washing results in the disintegration of the beads. Washing beads are allowed to dip in a CuSO4 solution and copper is cross-linked with the CMC chain via non-covalent interactions, resulting in the formation of well-developed CMC/ZnO/Ca/Cu cross-linked hydrogel bead, as portrayed in Fig. 5(v). The complexation and electrostatic interaction between the functional groups of the CMC chain and metal ions are responsible for the formation of stable cross-linked hydrogel bead.
 |
| Fig. 5 Plausible mechanism for the formation of well-developed hydrogel bead. | |
3.7 Study of the swelling and deswelling properties of hydrogel nanocomposites
3.7.1 Effect of cross-linker concentrations on the water absorption capacity of hydrogels (in distilled water). Fig. 6(a) depicts the effect of the cross-linker concentration on the swelling ratio of hydrogels as a function of time in distilled water. From the results of the tea bag method for the evaluation of the swelling ratio, there is an optimum range in the concentration of zinc chloride exists, where the SR is highest. A higher cross-linker concentration creates a huge number of growing polymeric chains with large cross-linking network systems, resulting in a lower SR. When the cross-linker density exceeds 0.3 g for zinc chloride, the SR decreases due to reduced space between the cross-linkers. From the swelling point of view, the MH-4 sample is considered as the best hydrogel in comparison to others. The equilibrium swelling ratio (Qeq) of hydrogel bead in distilled water is also shown in Fig. S11. An equilibrium swelling ratio is achieved by the hydrogel, when the osmotic pressure from swelling and elasticity of polymer is balanced. In smaller and greater concentrations of cross-linker than the optimum range, the swelling ratio of hydrogel decreases. The hydrogel sample takes time to reach the equilibrium SR. The Qeq values of MH-1, MH-2, MH-3, MH-4, MH-5 and MH-6 in distilled water were found to be (618 ± 42.19), (624 ± 21.7), (654 ± 26.42), (915 ± 40.6), (799 ± 51.01) and (698 ± 19.9), respectively. The swelling process of the hydrogel involves three complicated phenomena: initially, diffusion of water molecules into the hydrogel network occurs, and then, the hydrated polymer chain relaxes followed by the expansion of the polymer network into the surrounding medium.
 |
| Fig. 6 Swelling ratio of hydrogel bead in (a) distilled water and buffer of (b) pH 4, (c) pH 7 and (d) pH 9.2 (digital images are shown after 7 hours of swelling). | |
3.7.2 Effect of pH on the swelling ratio of hydrogels. The synthesized hydrogel still contains unreacted acid groups, which should be ionized by protonation in acid solutions. We measured the water uptake capacity at a certain interval of buffer at pH 4 [Fig. 6(b)], pH 7 [Fig. 6(c)] and pH 9.2 [Fig. 6(d)]. The results revealed that a relationship exists between the pH and the swelling capacity. The swellability of hydrogel bead is lowered during the initial periods at pH 4, and it can also be directly seen from the digital images of swollen hydrogel bead (Fig. 6). At 10 hours, the SR of MH-1, MH-2, MH-3, MH-4, MH-5 and MH-6 in pH-4 was found to be (926 ± 6.89), (937 ± 17.23), (953 ± 23.67), (976 ± 3.21), (930 ± 37.45) and (896 ± 22.6), respectively. The swelling ratio reduces with the reduction in the degree of ionization of gel-bound groups. At pH 7, during the first 5 hours, the gel swelled fast and then leveled off gradually and started to degrade. Similarly, after 10 hours of swelling, hydrogel bead at pH 9 also started to degrade. Moreover, the stability of hydrogel bead was higher in the basic medium. The hydrogel displays a lower value of SR content at acidic pH than at basic pH. When the pH of the swelling solution is higher than the pKa values of the carboxylic groups of CMC (pKa = 4.5), the carboxylic groups are ionized to COO− ions. Therefore, similar ions cause intermolecular repulsion, which ultimately leads to a state of swelling.52
3.7.3 Effect of the temperature and ionic strength swelling ratio of hydrogels. The influence of temperature on the swelling ratio of optimized hydrogel bead (MH-4) was investigated by the variation of temperature of swelling medium in the range of 5–50 °C in distilled water. The obtained results are summarized in Table S1. With the increase in temperature, the SR increases gradually up to 50 °C. This may be attributed to the fact that at higher temperatures, the segmental mobility, diffusion of water molecules and relaxation of the network chain are greater, resulting in an enhanced swelling ratio.53 Moreover, at higher temperatures, due to the breaking of hydrogen bonding interactions, the hydrogel bead absorb water to the maximum possible way. The liquid in which the hydrogel swelling occurs in real soil always contains a more or less wide set of dissolved salts. Considering the great impact of saline water on the swelling ratio of hydrogels and to expand their application in the agricultural field, the interaction of various salt solutions with the composite was investigated. Table S2 depicts the swelling ratio of hydrogel in 0.1 M NaCl, 0.1 M KCl and 0.1 M CaCl2 solutions, and the digital images of the swollen hydrogel after 24 hours of swelling in the saline medium are shown in (Fig. S12). The swelling ratio was found to be higher in NaCl, followed by KCl and CaCl2. Osmotic pressure plays a crucial role in the water absorption capacity of the hydrogel. As the electric charge between the ions in the solution decreases, the absorption increases. Therefore, NaCl and KCl have a higher SR than that of CaCl2. The lower the radius of the same valent cation (Na+ < K+), the water absorption capacity is more. As the size of the ions in the swelling medium increases, there is a difficulty in the penetration of ions within the hydrogel matrix.54,55
3.7.4 Swelling kinetics of the hydrogel (in distilled water). Swelling kinetics is an important property to analyze and study the application of hydrogel in diverse fields. The swelling mechanism of the hydrogel greatly depends on the equilibrium water content, the chemical composition of hydrogel and the swelling rate. To explain swelling kinetics, two empirical equations, namely, Fickian diffusion (eqn (2)) and second-order kinetic (eqn (3)) models were applied as explained in Section 2.5. The swelling kinetics graph for the hydrogel in distilled water is shown in Fig. 7, and the individual kinetic graphs of all the hydrogel bead are shown in (see Fig. S13 and S14). From the diffusion exponent value (n) of the Fickian diffusion model, three different mechanisms could be anticipated, the value of ‘n’ can be determined from the slope of the straight line obtained from eqn (2), where the swelling data has not yet obtained the equilibrium, only 60% of water enters in the hydrogel structure. When ‘n’ is less than 0.5, Fickian Diffusion is predominant and the concentration gradient is the cause for water transport. For 0.5 < n < 1, non-Fickian diffusion is dominant, and for n > 1, the relaxation of the polymer chain is followed by an anomalous diffusion mechanism.56 From Table S3, it is seen that the value of n for most of the hydrogel bead is less than 0.5, indicating that the hydrogel follows the Fickian diffusion mechanism. Thus, the swelling is controlled by the diffusion of water into the polymer. Moreover, the co-relations co-efficient (R2) for all the samples in the Fickian Diffusion model is less than 0.95, except for MH-4 and MH-5, as shown in Fig. 7; therefore, second-order kinetics was analyzed. It can be observed that the second-order kinetics represents a good linear corelation coefficient for all the hydrogel bead, indicating the high reliability of this model. The results indicate that under the optimized condition, i.e., for the MH-4 sample, the R2 value is found to be 0.9904, suggesting that this equation offers a more suitable fit for the swelling mechanism. From the second-order kinetic model, the theoretical value of Qeq was also determined, and it is closely related to the experimental value, as shown in Table S4. Using second order kinetic model, the initial swelling rate constant (Kis) and swelling rate constant (Ks) are also determined and their values are shown in Table S4.
 |
| Fig. 7 Swelling kinetics of the hydrogel: (a) Fickian diffusion model and (b) second-order kinetics. | |
3.7.5 Study the deswelling and recyclability tests. After achieving the maximum swelling ratio, the hydrogel samples were removed from the distilled water medium and allowed to stand under open-air conditions to study their deswelling properties. One of the most important qualities of soil fertilizer that carries hydrogels is its capacity to retain huge amounts of water for a long duration of time. The decrease in the swelling ratio (%) of the hydrogel during the de-swelling process as a function of time is shown in Fig. S15(a). Moreover, the initial de-swelling rate is very fast, i.e., in the first ten hours, the CMC@CC shows ∼22% of weight loss. It is clear from the figure that the hydrogel takes time to reach its original weight. The de-swollen hydrogel was further allowed to undergo swelling–deswelling cycles. The water retention capacity was measured by the intermolecular interactions, including hydrogen bonding, hydrophobic interactions and electrostatic interactions in water solutions, which are directly related to the macromolecular structure and the state of water. Three types of water, i.e., free water, bound and semi-bound water are associated with different interactions with the hydrogel during swelling. During deswelling, free water is initially removed as it is physically entrapped in the hydrogel matrix. Bound water directly forms hydrogen bonds with carboxylic or hydroxy groups of CMC and may form electrostatic ion-dipole interactions with carboxylate anion (–COO−), and it is responsible for osmotic swelling. This water cannot easily be released from the hydrogel and is responsible for the high-water-retention behavior. Semi-bound water exhibits intermediate properties between free and bound water.57 We studied four such repetitive cycles and found that the hydrogel maintains its properties throughout these cycles. The SR (%) slightly dropped under each cycle (as shown in Fig. S15(b)) due to the weakening of the hydrogen bonds. Deswelling may cause structural relaxation or rearrangement of the polymer matrix, which can slow the swelling behavior in the next cycle. Repetitive swelling–deswelling may break some cross-linking points, which may reduce the possible hydrogen bonding interaction with water and lower the swelling capacity over multiple cycles.
3.8 Biodegradability test
The biodegradation process can be comprised of mainly three stages of degradation. In the first phase of degradation, microorganisms participate in the degradation of bio-based materials of hydrogel and boost the degradation process. Moreover, the degradation stage was slow in the second phase due to increase in the water content of the hydrogels, which, in turn, restricted oxygen transfer to the hydrogel bead. It generates an anaerobic environment and, hence, slows the microbial growth. However, in the final stage, the hydrogel bead are converted into their simplest form, where complete degradation of the polymer backbone occurs.58 Fig. S16(a) shows the biodegradation profile of both CMC@CC and NCMC@CC, and the degradation percentage was calculated using eqn (S5). Furthermore, Fig. S16(b) depicts the digital images of both the hydrogel bead after one month of application. According to the results obtained from the soil burial method, decomposition occurs very slowly in the initial stage. On the 10th day, the percentage of degradation for CMC@CC and NCMC@CC was found to be ∼98% and ∼97%, respectively. After one month, the degradation turned ∼94% and ∼96% for CMC@CC and NCMC@CC, respectively. The slow biodegradation profile confirms that the prepared beads are suitable for agricultural delivery. To date, we have found only limited literature on the application of CMC/Zn/Ca cross-linked hydrogels for agricultural purposes. Akalin et al. prepared zinc-loaded CMC/FeCl3 and carrageenan/glutaldehyde cross-linked hydrogels and examined their effectiveness on the growth of wheatgrass.59 Sharif et al. used CMC as a coating material to modify the controlled release behavior of a zinc/aluminium layered double hydroxide, quinclorac.60 Our work offers distinct advantages over the existing studies. Here, micronutrients, i.e., Zn, Ca and Cu, are participating in the cross-linking process; therefore, these are released to the soil only after degradation.
3.9 Study of the cumulative release and release mechanism of hydrogels
3.9.1 Release of nutrients in water. Potassium nitrate was selected as a model fertilizer due to its pH-independent solubility, i.e., it does not alter the pH of the release medium. Nitrate loading was performed through the sorption process, and the loading percentage was calculated using eqn (4). The comparison of nitrate release from NCMC@CC with standard potassium nitrate in distilled water as a function of time is presented in Fig. 8(a). There are three main steps to monitor the nutrient release rate from the hydrogel matrix: liquid perception of the fertilizer, dissolution of the nutrient and diffusion of nutrients from the hydrogel matrix. Mostly, the fertilizer release arises due to the enlargement and loosening of the polymer network of the hydrogel.61 At the initial release stage, the nitrate release rate is high, due to the higher difference in concentration gradient of nitrate between those inside the hydrogel bead with the surrounding medium.62 Moreover, nitrate was loaded into the hydrogel via the sorption process. As both copper and calcium are in +2 oxidation state within the hydrogel matrix, there is a strong possibility of ionic interactions or other non-covalent bonding interactions between these ions with nitrate. These interactions may help the slow nutrient release of nutrients from hydrogel bead. It is seen that ∼55% of nitrate was released from the nanocomposite hydrogel bead within 15 hours, while the standard potassium nitrate released almost ∼100% of nitrate within a few minutes. The nutrient release process is characterized by an S-shaped curve, and the nutrient release percentage is varied throughout the whole process. Other researchers also observed similar nitrate release patterns. Ibrahim et al. synthesized Ca2+ cross-linked alginate/CMC hydrogel bead for the slow release of ammonium nitrate. They found that 85% of fertilizer was released within 24 hours at pH 7, when hydrogel bead were loaded with 10% of ammonium nitrate.63 In another study, Mahdavinia et al. examined that in the first 40 minutes, 76% or 64% potassium nitrate was released from a porous hydrogel that is made up of polyacrylamide.64
 |
| Fig. 8 (a) Comparison of the cumulative release profile of nitrate from NCMC@CC with standard potassium nitrate. (b) Digital images showing the inhibition zone diameter against R. solanacearum. | |
3.9.2 Nutrient release kinetics. To obtain a more quantitative understanding of the nitrate release kinetics, the release data were analyzed using four kinetic models: zero-order, first-order, Higuchi and Korsmeyer–Peppas models, as described in (see Section S2). The kinetic plots for all the equations are presented in Fig. S17, and the obtained data are summarized in Table 2. From Fig. S17, it is seen that zero-order and Higuchi models are almost inappropriate for determining the nitrate release mechanism. The kinetic data suggested the linear fitting of the Korsmeyer–Peppas model with an R2 value of 0.962. In this model, the value of the diffusion coefficient “n” provides information about the undergoing transport mechanism. The value of n ≤ 0.43 indicates Fickian diffusion and n < 0.43 < 0.85 indicates non-Fickian diffusion kinetics for the release of nitrate. However, n > 0.85 signifies a case II transport mechanism.62 Here, the value of n is 0.36, indicating that Fickian diffusion is predominant, and, therefore, the diffusion of nitrate ion through the lattice structure of the hydrogel is the limiting factor to regulate the release process. A similar type of nitrate release profile was also reported by Juan et al.65
Table 2 Kinetics parameters (R2, K1, KP and n) of the first-order and Korsmeyer–Peppas model
Kinetics models |
R2 |
K1 |
KP |
n |
First order |
0.331 |
0.001 |
— |
— |
Korsmeyer–Peppas |
0.962 |
— |
0.050 |
0.360 |
3.10 In vitro antibacterial activity
The in vitro antibacterial properties of CMC@CC were tested against R. solanacearum. The inhibition zone under and around the tested sample for the bacterial growth was detected visually, and the zone of inhibition (ZOI) results of the application of CMC@CC are shown in Fig. 8(b). Growth inhibition of R. solanacearum can be observed for CMC@CC treatment, whereas in the control group, there is complete growth of bacteria within 48 hours (Fig. S18(a)). The measured individual inhibition zone diameter for each replicate is shown in Table S5, and their digital images are shown in Fig. S18(b). The average ZOI was found to be (13.2 ± 2.53)
mm, and the size and consistency of this inhibition zone depend on the size of the beads. From the results, we revealed that R. solanacearum has been controlled successfully using our prepared hydrogel bead under in vitro conditions. Moreover, the visual changes were also observed in R. solanacearum after the application of CMC@CC, as characterized by a colour change from white to yellow. In the literature, various pesticide formulations are available to control the plant pathogen bacteria, R. solanacearum. Pradhanang et al. conducted a greenhouse experiment using plant essential oils, including thymol, palmarosa oil, and lemongrass, to suppress the bacterial population and minimize the wilt incidence of the tomato plant.32 Elsayed et al. examined the antagonistic behaviour of bacterial strains Bacillus velezensis (B63) and Pseudomonas fluorescens (P142) against this plant pathogen under both in vitro and in vivo conditions. These biocontrol agents under field conditions significantly decrease the bacterial densities in the rhizosphere and in tomato shoots.33 Chen et al. fabricated a surfactant-stabilized Ag nanoparticle,66 and Yang et al. used hydroxycoumarin as a promising antibacterial agent for this pathogen.67 Ma et al. prepared a tetramycin-loaded pH-responsive adipic dihydrazide (ADH) and Ca2+ cross-linked oxidized sodium alginate-based gel as a carrier of pesticides.68 Most of the existing formulations have some limitations. For example, for better performance, we must provide a suitable environment for bacteria, which itself is challenging for the viability and growth of the bacteria. Moreover, neither Ag nor tetramycin is essential for the growth of plants. This work aimed to minimize the limitations of pesticide administration to control this plant pathogen, and we believe that, as our prepared hydrogel bead contains only plant nutrients, it has application potential in the near future.
3.11 Study of the growth of Solanum lycopersicum L.
To investigate the practical application of these hydrogel bead as a package of nutrients, plant trials on Solanum lycopersicum L. were performed. The application of nanocomposites to soil ameliorates the adverse effects of chemical fertilizer on soil. Fig. 9(a) displays the digital images of plant growth in terms of plant height using different fertilization methods. Fig. 9(b) and (c) show the comparison of stem length, root length, plant height and plant biomass with the control. It was observed that tomato plants placed in soil treated with NCMC@CC showed a stem length of 80 mm, while control soil produced a stem length of 50.8 mm. The greatest plant height corresponding to NCMC@CC and CMC@CC were 89.8 mm and 71.0 mm, respectively, larger than that of the control (50 mm). The root length and dry weight of tomato plants treated with NCMC@CC were also increased as compared to the control. Potassium nitrate has a significant affect the growth process, and this difference was visible in NCMC@CC. It was evident that the application of NCMC@CC benefited plant growth more than that of CMC@CC. This detailed analysis was observed under sufficient water conditions. CMC@CC contains zinc, calcium and copper, which may be responsible for these early growth parameters. NCCMC@CC contains nitrate as a major fertilizer, which enhances plant growth. Moreover, the synergitic effect or positive interrelationship between macro- and micronutrients may also be responsible for the growth parameters. Therefore, the prepared hydrogel bead may have potential application prospects in agriculture to enhance crop productivity. Moreover, the physiological properties of the soil were also examined after collecting the tomato plants. The changes in pH and electrical conductivity of soil in comparison to the control are shown in Fig. 9(d). There is hardly a change in the above-mentioned parameters, indicating that our prepared nanocomposite hydrogel has maintained soil fertility throughout the trial periods. Moreover, one-way ANOVA followed by the LSD test was used to determine the statistical significance of different treatments, and is explained in Section S18.
 |
| Fig. 9 (a) Digital images of plant growth using different treatments. Comparison of (b) stem length and root length, (c) plant height and plant biomass of different treatments and (d) changes in soil physiological properties after application of different treatments. | |
4. Conclusion
The objective of the study was to develop a new superabsorbent material based on carboxymethyl cellulose, which could be further reinforced and cross-linked with calcium and copper, and loaded with nitrate to make it a multi-nutrient package for plants. The results obtained during experimental and mathematical analyses showed that 0.22 M of cross-linking agent (i.e., zinc chloride) is suitable for preparing the best hydrogel. From the FTIR spectra, XRD patterns and SEM images, we can confirm the in situ formation and distribution of nano ZnO within the hydrogel matrix. To analyze the nitrate release mechanism in water, we evaluated the fractional release data from the static release experiment by fitting the curve of fractional release using four mathematical models. Copper cross-linking is essential for enhancing the slow-release behavior of nutrients and the water retention properties of the hydrogel. The cross-linking ratio revealed a significant effect on the swelling ratio of hydrogels. The maximum swelling ratio under optimized conditions in distilled water was found to be 915% against MH-4 samples. The application of the prepared hydrogel composite shows the statistical significance of the growth pattern of tomato plants as compared to the control. In vitro study against R. Solanacearum of the prepared hydrogel bead reveals its antagonistic behavior in controlling the bacterial wilt disease of the tomato plant. These materials not only satisfy the demand of the economic and environmental sustainability market but also go a long way towards fulfilling future requirements to synthesize renewable biodegradable polymers in the nanotechnology concept. In addition, due to the combination of different macro- and micro-nutrients, the prepared hydrogel composites have emerged as one of the most promising polymeric materials for the efficient delivery of agrochemicals. The dual role of hydrogel bead, providing water and nutrients, while possessing bactericidal properties, makes them potential candidates for promoting agricultural sustainability.
Author contributions
Madhusmita Baruah: data curation, formal analysis, investigation, methodology, writing – original draft; Rimjim Gogoi: data curation, formal analysis, investigation, methodology, writing – original draft; Tanmoy Karak: data curation, formal analysis, investigation, methodology, writing – review and editing; Sangita Bharali: data curation, formal analysis; Anurag Kashyap: data curation, formal analysis; Jiban Saikia: conceptualization, funding acquisition, methodology, project administration, resources, validation, visualization, writing – review and editing.
Conflicts of interest
The authors declare no competing financial interest.
Data availability
The data supporting this article have been included as part of the SI.
Digital images of hydrogel bead; fertilizer release kinetics; FTIR spectra of KNO3 and NCMC@CC; SEM micrograph and SEM-EDX of CMC@C; cross-sectional SEM micrograph and SEM-EDX of CMC@CC; SEM-EDX spectra of CMC@CC in both swollen and dry forms; rheological analysis; XRD of CMC; TGA, DSC and DTA thermogram of CMC; DTA of CMC, CMC@CC and NCMC@CC; full-scan XPS survey of CMC@CC and NCMC@CC; equilibrium swelling ratio of hydrogel bead; de-swelling property and repetitive swelling cycle of hydrogel bead; swelling kinetics graphs for the hydrogel using the Korsmeyer–Peppas model and second-order kinetic model; swelling kinetic parameters for the Fickian diffusion and second-order kinetic models; study of the stimuli responsive behavior of hydrogels; determination of SR (%) of CMC@CC in a saline medium (NaCl, KCl and CaCl2) after 24 hours of swelling; comparison of the digital images of CMC@CC in different saline media; biodegradation study of hydrogel bead; release kinetics of nitrate in water (zero-order, first-order, Higuchi model and Korsmeyer–Peppas model); antibacterial activity and statistical analysis of plant growth. See DOI: https://doi.org/10.1039/d5tc01581b
Acknowledgements
The authors declare that financial support was received for the research, authorship and/or publication of this article. J. S. thanks DST-PURSE program [under project no. SR/PURSE/2022/143(C)], DBT [under project no. BT/PR36255/NNT/28/1728/2020] and DST SERB-SURE program [under project no. SUR/2022/001492 and under the DST-FIST (SRF/FST/CS-l/2020/152)] for the financial support. The authors are immensely grateful to the Dibrugarh University for providing all the infrastructural facility. The authors are also thankful to UGC, New Delhi, for Special Assistance Programme (UGC-SAP) to the Department of Chemistry, Dibrugarh University. Finally, we wish to record our thanks and gratitude to the anonymous reviewers for their valuable suggestions that helped us a lot in improving this manuscript.
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