T. M. Tingab,
Mohamed Mahmoud Nasef*cd and
Kamaruddin Hashimb
aFaculty of Chemical Engineering (FChE), Universiti Teknologi Malaysia, UTM, 81310, Johor Bahru, Johor, Malaysia
bRadiation Processing Technology Division, Malaysian Nuclear Agency, 43000, Kajang, Selangor, Malaysia. E-mail: tmting@nm.gov.my
cMalaysia-Japan International Institute of Technology (MJIIT), Universiti Teknologi Malaysia, Jalan Semarak, 54100, Kuala Lumpur, Malaysia
dInstitute of Hydrogen Economy, Universiti Teknologi Malaysia, Jalan Semarak, 54100, Kuala Lumpur, Malaysia. E-mail: mahmoudeithar@cheme.utm.my; Fax: +603 22031463
First published on 8th April 2015
A new adsorbent containing boron-selective groups was prepared by radiation induced grafting of vinyl benzyl chloride (VBC) onto nylon-6 fibers followed by functionalisation with N-methyl-D-glucamine (NMDG). The density of glucamine loaded in the adsorbent was tuned by optimisation of the reaction parameters such as NMDG concentration, reaction temperature, reaction time and degree of grafting using response surface methodology (RSM) employing Box–Behnken design (BBD). The optimum parameters for achieving the maximum glucamine density (1.7 mmol g−1) in the adsorbent are 10.6%, 81 °C, 47 min and 121% for the NMDG concentration, reaction temperature, reaction time and degree of grafting (DG), respectively. The deviation between the optimum experimental and predicted glucamine density is found to be 1.2% suggesting the reliability of RSM in predicting the yield and optimising the functionalisation reaction parameters. The chemical composition, morphology and structure of the NMDG-containing fibrous adsorbent were studied using Fourier-transform infrared (FT-IR) spectroscopy, scanning electron microscopy (SEM) and X-ray diffraction (XRD), respectively. The thermal properties were determined using differential scanning calorimetry (DSC) and the thermal stability was evaluated by thermogravimetric analysis (TGA). Considering the physico-chemical properties of the fibrous adsorbent and the preliminary results of boron adsorption, it can be suggested that this adsorbent is a promising candidate for boron removal.
Various technologies have been used to remove boron from different streams including precipitation–coagulation, chemical adsorption, physical adsorption, electro-dialysis, liquid–liquid extraction, reverse osmosis, electro-coagulation and ion exchange.2 Of these, ion exchange is the most effective and preferable method for removing boron to meet the required levels compared to other separation methods.3 Chelating/ion exchange resins represent the central component in ion exchange systems and their distinct affinity towards boron is crucial for the viability of ion exchange treatment of boron-contaminated streams.
Commercial boron chelating resins and their researched counterparts based on functionalised polymers mostly contain N-methyl-D-glucamine (NMDG). This functional group exhibits a high selectivity towards boron due to the presence of five hydroxyl groups allowing for the coordination of boron to form a stable complex.4 Therefore, the majority of researched adsorbents are obtained by the functionalisation of adsorbent precursors with NMDG.3
Various polymer-based adsorbents have been developed for boron removal from solution using various polymerisation routes.5–12 A review of various strategies for the preparation of alternative polymer-based adsorbents and their performance evaluation was published recently.3 Among all, adsorbents obtained by radiation-induced grafting and subsequent functionalisation provide attractive materials for more effective removal of ionic pollutants from water and wastewater.13 Radiation-induced grafting is used for the preparation of such desired materials due to its simplicity and as it does not require catalysts or initiators, thus leaves no detrimental residues. Moreover, the grafting reaction can be initiated from monomers in different phases and temperatures allowing either surface or bulk modification of polymer substrates depending on the reaction parameters which can be tuned to obtain the desired compositions. Various polymer substrates such as fibers, fabrics and films can be modified with a variety of functional groups in large quantities.13,14 Particularly, radiation grafted adsorbents having a fibrous structure with high selectivity and a large surface area overcome the diffusion limitations associated with the conventional granular resins and showed a promising performance for the removal of pollutants such as heavy metal ions15 and phosphate as well as arsenic species.16
Removal of boron by fibrous adsorbents grafted with glycidylmethacrylate (GMA) onto various fibers such as polypropylene and viscose fibers,9 nylon-6 fibers,17 polyethylene (PE)18 fibers and PE non-woven fabric19 followed by NMDG treatment was reported recently. The fibrous chelating adsorbents showed a higher adsorption capacity and faster kinetics together with a tolerance to high flow speed with a small drop in the breakthrough capacity compared to chelating granular resins.8,9,19 However, these adsorbents are challenged by degradation (leaching of functional groups) during the regeneration process in addition to deterioration of their mechanical properties caused by the incorporation of excessive amounts of amorphous poly(GMA) during grafting to impart a high glucamine content leading to a fragile structure.
To improve the chemical and mechanical stability of the fibrous adsorbents, vinyl-benzyl chloride (VBC) monomer has been grafted as an alternative monomer to confer more stable benzyl arms to a favourable fibrous substrate (nylon-6 fibers) capable of hosting glucamine through a facile functionalisation reaction. VBC has neither been radiation grafted on nylon-6 fiber nor used for the preparation of fibrous adsorbents for boron removal. The selection of nylon-6 as a substrate is due to its outstanding physico-mechanical properties and low cost.20 Moreover, it has a moderate radiation resistance where it undergoes crosslinking and chain scission. The extent of each radiolytic reaction depends on the adsorbed dose and irradiation atmosphere.21 Crosslinking, which takes place in nylon-6 during irradiation, is reported to improve the mechanical properties compared to original nylon-6.20 Thus, it is of high interest to tune the content of the glucamine groups to minimize the impact of the applied preparation procedure (grafting and functionalisation) on the properties of the nylon-6 fibrous substrate. This can be achieved by modelling the functionalisation reaction, optimisation of its parameters and prediction of the reaction yield using statistical tools.
The response surface method (RSM) developed by Box and Wilson22 is a mathematical expression to describe the relationship of a few independent variables with one or more responses. RSM is based on fitting mathematical models to the experimental results generated from a designed experiment to verify the model obtained. When the model is identified, optimisation and predictions of the experimental parameters such as variables and responses can be derived according to requirements. These include improving the process performance, identifying significant relationships of parameters, reducing operational costs and minimizing the experimental time.23 The developed experimental design is based on three-level (+1, 0, −1) incomplete factorial designs which take the interactions of variables into account.24
The objective of this study was to prepare a new boron-selective adsorbent with a tuned content of glucamine groups. This was carried out by radiation-induced grafting of VBC onto nylon-6 fibers followed by functionalisation with NMDG under optimised parameters determined through the RSM. The properties of the prepared NMDG-containing fibrous adsorbent were evaluated using scanning electron microscopy (SEM), Fourier transform infrared (FT-IR) spectroscopy, differential scanning calorimetry (DSC), thermogravimetric analysis (TGA), X-ray diffraction (XRD) and a universal mechanical tester with reference to the original and poly(VBC)-grafted nylon-6 fibers. The obtained adsorbent was tested for the removal of boron from solutions for various pH values and adsorption/desorption cycles.
The degree of grafting (DG) was calculated from the weight increase by:
![]() | (1) |
Fig. 1 shows a scheme for the grafting of VBC onto nylon-6 fibers and the functionalisation of poly(VBC) grafted fibers with NMDG. The density of glucamine groups loaded on the adsorbent was calculated by:
![]() | (2) |
The independent variables for the present reaction include the NMDG concentration (X1), reaction temperature (X2), reaction time (X3) and degree of grafting (X4). The response or the dependent variable is the density of glucamine groups. A four factors at three levels and 29 runs BBD experimental design was applied to derive a quadratic polynomial equation to predict the optimum combination of independent variables to tune the glucamine content in the adsorbent. The 29 experimental runs of BBD composed of 16 factorial points, 8 axial points and 5 replicates at the center points. The selection ranges of the respective variable were coded as −1, 0, and +1 corresponding to the low level, mid-level and high level as shown in Table 1. The experimental ranges selected for the independent variables were: 5, 10 and 15 wt% for the NMDG concentration, 70, 80 and 90 °C for the reaction temperature, 10, 35 and 60 min for the reaction time and 70, 100 and 130% for the degree of grafting. Table 2 shows the design arrangement and the actual experimental design matrix. The Design-Expert software (Version 6.0.8, Stat-Ease, Inc., USA) was employed to analyse the experimental results.
Variables | Code | Level values | Factor values |
---|---|---|---|
NMDG concentration (wt%) | X1 | −1, 0, 1 | 5, 10, 15 |
Reaction temperature (°C) | X2 | −1, 0, 1 | 70, 80, 90 |
Treatment time (min) | X3 | −1, 0, 1 | 10, 35, 60 |
DG (%) | X4 | −1, 0, 1 | 70, 100, 130 |
Runs | NMDG (X1) | Temperature (X2) | Time (X3) | DG (X4) | Functional group density (mmol g−1-adsorbent) | |
---|---|---|---|---|---|---|
(wt%) | (°C) | (min) | (%) | Actual | Predicted | |
1 | 5 | 70 | 35 | 100 | 1.37 | 1.39 |
2 | 15 | 70 | 35 | 100 | 1.51 | 1.53 |
3 | 5 | 90 | 35 | 100 | 1.46 | 1.47 |
4 | 15 | 90 | 35 | 100 | 1.60 | 1.61 |
5 | 10 | 80 | 10 | 70 | 0.95 | 0.98 |
6 | 10 | 80 | 60 | 70 | 1.41 | 1.40 |
7 | 10 | 80 | 10 | 130 | 1.27 | 1.30 |
8 | 10 | 80 | 60 | 130 | 1.70 | 1.69 |
9 | 5 | 80 | 35 | 70 | 1.27 | 1.27 |
10 | 15 | 80 | 35 | 70 | 1.40 | 1.40 |
11 | 5 | 80 | 35 | 130 | 1.56 | 1.57 |
12 | 15 | 80 | 35 | 130 | 1.70 | 1.71 |
13 | 10 | 70 | 10 | 100 | 1.11 | 1.13 |
14 | 10 | 90 | 10 | 100 | 1.16 | 1.18 |
15 | 10 | 70 | 60 | 100 | 1.52 | 1.51 |
16 | 10 | 90 | 60 | 100 | 1.63 | 1.62 |
17 | 5 | 80 | 10 | 100 | 1.15 | 1.10 |
18 | 15 | 80 | 10 | 100 | 1.30 | 1.24 |
19 | 5 | 80 | 60 | 100 | 1.48 | 1.51 |
20 | 15 | 80 | 60 | 100 | 1.63 | 1.65 |
21 | 10 | 70 | 35 | 70 | 1.31 | 1.30 |
22 | 10 | 90 | 35 | 70 | 1.35 | 1.34 |
23 | 10 | 70 | 35 | 130 | 1.59 | 1.57 |
24 | 10 | 90 | 35 | 130 | 1.70 | 1.68 |
25 | 10 | 80 | 35 | 100 | 1.57 | 1.57 |
26 | 10 | 80 | 35 | 100 | 1.57 | 1.57 |
27 | 10 | 80 | 35 | 100 | 1.57 | 1.57 |
28 | 10 | 80 | 35 | 100 | 1.57 | 1.57 |
29 | 10 | 80 | 35 | 100 | 1.57 | 1.57 |
ANOVA was used to analyse the experimental data. The coefficient of determination (R2), adjusted coefficient of determination and predicted coefficient of determination analysis were calculated to test the adequacy of the developed models. After fitting the models, the generated data were used to generate response surfaces and contour plots. All statistical analyses were conducted using Design-Expert software (Version 6.0.8, Stat-Ease, Inc., USA).
FT-IR analysis was conducted using a PerkinElmer Spectrum One FT-IR spectrometer. The samples were scanned in the transmission mode with a resolution of 4 cm−1 and wave number range of 500 to 4000 cm−1.
XRD analysis was carried out using an X’pert Pro X-ray diffractometer model PW 3040 by Philips. The measurements were performed using CuKα radiation, 2θ degrees in the range of 10–80° and a counting time of 2 s. The applied voltage and current were fixed at 40 kV and 30 mA, respectively. The X-ray wavelength was fixed at 1.54 Å.
DSC measurements were performed using a Mettler-Toledo, DSC-822e calorimeter. The thermal analysis was conducted in the temperature range of 30–300 °C at a heating rate of 10 °C min−1 under a N2 atmosphere.
TGA analysis was carried out using a PerkinElmer model TGA-STA6000. The analysis was performed in the temperature range of 35–800 °C at a heating rate of 10 °C min−1 and under a N2 atmosphere.
The tensile strength and displacement were measured using an Instron universal tester (Model 4301) operated at a 10 mm min−1 crosshead speed according to ASTM D3822-07. The reported values are averages of five sample measurements.
The effect of adsorbent dose variation on the boron removal efficiency was investigated by changing the weight in the range of 0.05–1.00 g. The experiments were carried out using 30 mL of boric acid solution with two different concentrations of 100 and 200 mg L−1, a temperature of 30 °C, stirring speed of 200 rpm and reaction time of 2 h.
The elution (desorption) experiments were carried out by equilibrating the boron loaded adsorbent with a 1 M HCl solution to test the reusability of the adsorbent.
In all the adsorption experiments, the concentration of boron in the solutions was determined using a PerkinElmer Optima 7300 DV ICP-OES.
The adsorption capacity (q), which is the amount of ions adsorbed per unit mass of the adsorbent was calculated using eqn (3).
![]() | (3) |
![]() | (4) |
Source | Prob > F | Std. dev. | R2 | Adjusted R2 | Predicted R2 | Press | Remarks |
---|---|---|---|---|---|---|---|
Linear | <0.0001 | 0.092 | 0.8070 | 0.7749 | 0.7327 | 0.28 | — |
Interactive (2FI) | 0.9998 | 0.110 | 0.8093 | 0.7033 | 0.5265 | 0.50 | — |
Quadratic | <0.0001 | 0.030 | 0.9880 | 0.9761 | 0.9311 | 0.07 | Suggested |
Cubic | 0.2481 | 0.025 | 0.9965 | 0.9835 | 0.4904 | 0.54 | Aliased |
The final model obtained in coded variables in which X1, X2, X3 and X4 are in sequence representing the NMDG concentration, reaction temperature, reaction time and DG, is given as:
Y = 1.57 + 0.071X1 + 0.041X2 + 0.20X3 + 0.15X4 + 0.0025X1X4 + 0.015X2X3 + 0.017X2X4 − 0.0075X3X4 − 0.028X12 − 0.043X22 − 0.17X32 − 0.056X42 | (5) |
Source | Sum of squares | DF | Mean square | F-value | Prob > F | Remarks |
---|---|---|---|---|---|---|
Model | 1.04 | 14 | 0.074 | 82.61 | <0.0001 | Significant |
X1 | 0.060 | 1 | 0.060 | 66.81 | <0.0001 | |
X2 | 0.020 | 1 | 0.020 | 22.20 | 0.0003 | |
X3 | 0.49 | 1 | 0.49 | 546.03 | <0.0001 | |
X4 | 0.28 | 1 | 0.28 | 309.67 | <0.0001 | |
X12 | 5.207 × 10−3 | 1 | 5.207 × 10−3 | 5.78 | 0.0306 | |
X22 | 0.012 | 1 | 0.012 | 13.52 | 0.0025 | |
X32 | 0.18 | 1 | 0.18 | 203.95 | <0.0001 | |
X42 | 0.020 | 1 | 0.020 | 22.44 | 0.0003 | |
X1 X2 | 0.000 | 1 | 0.000 | 0.000 | 1.0000 | |
X1 X3 | 0.000 | 1 | 0.000 | 0.000 | 1.0000 | |
X1 X4 | 2.500 × 10−5 | 1 | 2.500 × 10−5 | 0.028 | 0.8701 | |
X2 X3 | 9.000 × 10−4 | 1 | 9.000 × 10−4 | 1.00 | 0.3346 | |
X2 X4 | 1.225 × 10−3 | 1 | 1.225 × 10−3 | 1.36 | 0.2631 | |
X3 X4 | 2.250 × 10−4 | 1 | 2.250 × 10−4 | 0.25 | 0.6251 | |
Residual | 0.013 | 14 | 9.012 × 10−4 | |||
Lack of fit | 0.013 | 10 | 1.262 × 10−3 | |||
Pure error | 0.000 | 4 | 0.000 | |||
Cor total | 1.05 | 28 |
The F value for the model was found to be high (82.61) with a low probability value of p < 0.0001. This suggests that the computed Fisher’s variance ratio was significant and has a high degree of adequacy for the quadratic model. The value of R2 was 0.9880 and this indicates that 95% of the experimental data were compatible. The adjusted R2 value was 0.9761 and this confirms the significance of the model. The predicted R2 value was 0.9311 suggesting a reasonably good correlation between the observed and predicted values. According to Mourabet et al.,25 if the difference between the adjusted R2 and predicted R2 is within 0.20, the predicted R2 is in reasonable agreement with the adjusted R2. Moreover, the adequate precision is a measure of the signal to noise ratio and a ratio greater than a value of 4 is desirable.25 The recorded adequate precision value in this study was 34, which indicates the presence of an adequate signal to noise ratio. The coefficient of variance (CV) value was found to be 2.07%, which is low and also indicates the accuracy and reliability of the experimental results.26
The data were analysed to check the normality of the residuals and the normal probability plot of the studentised residuals is shown in Fig. 2. It can be observed that the data points fit a straight line reasonably. This suggests that the model is established and the results of the ANOVA analysis obtained in this study are adequate and valid.
The 3D response surface plot of the variation of the glucamine density with NMDG concentration and temperature at a constant reaction time of 47 min and DG of 121% is shown in Fig. 3b. The glucamine density increased with the increase of the NMDG concentration and temperature where both parameters affected the glucamine density in a similar manner.
A maximum glucamine density was recorded at the NMDG concentration of 11 wt% and temperature of 82 °C beyond which no further increase takes place despite the increase in parameter values.
Fig. 3c shows a 3D surface plot of the glucamine density versus NMDG concentration and time at the reaction temperature of 81 °C and DG of 121%. The increased NMDG concentration and time result in an increase of the glucamine density. The reaction time of 40 min gave a maximum glucamine density beyond which it starts to level off and reach saturation.
Fig. 4 shows the Ramp report, which summarises the optimum predicted values for the independent variables leading to the maximum glucamine density using the BBD model. The optimum reaction parameters for achieving a glucamine density of 1.72 mmol g−1-adsorbent with a desirability function value of 1.000 are 10.6% NMDG concentration, 81 °C reaction temperature, 47 min reaction time and 121% DG.
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Fig. 5 SEM images of (a) original nylon-6 fibers, (b) poly(VBC) grafted nylon-6, 130% DG, and (c) glucamine functionalised poly(VBC) grafted nylon-6 fibers with 1.7 mmol g−1-adsorbent. |
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Fig. 6 FT-IR spectra of the original nylon-6, poly(VBC) grafted nylon-6 and NMDG functionalised poly(VBC) grafted nylon-6 fibers with different densities in the range of 1500–3700 cm−1. |
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Fig. 7 FT-IR spectra of the original nylon-6, poly(VBC) grafted nylon-6 and NMDG functionalised poly(VBC) grafted nylon-6 fibers with different densities in the range of 600–1500 cm−1. |
Band (cm−1) | Assignment |
---|---|
3300 | Hydrogen-bonded NH stretching |
3086 | NH Fermi resonance |
2931 | CH2 asymmetric stretching |
2859 | CH2 symmetric stretching |
1645 | Amide I |
1544 | Amide II |
1369 | Amide III + CH2 wagging |
1264 | Amide III + CH2 wagging |
1236 | CH2 wagging/twisting |
1203 | Amide III + CH2 wagging |
1170 | CONH skeletal motion |
1121 | CC stretching (amorphous) |
1072 | CC stretching |
974 | CONH in-plane (γ) |
929 | CONH in-plane (α) |
728 | Amide V (γ) |
705 | Amide V (α) |
Similar glucamine characteristic bands were reported in the literature for the synthesis of polymer/clay nanocomposite ion exchange resins based on NMDG for arsenic removal.29
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Fig. 8 X-ray diffraction profiles of the nylon-6, poly(VBC) grafted nylon-6 and glucamine functionalised poly(VBC) grafted nylon-6 with various densities. |
It is worth mentioning that the observation obtained from X-ray analysis is going along with the findings of FT-IR discussed earlier. Particularly, the incorporation of poly(VBC) onto nylon-6 fibers caused a major reduction in the overall crystallinity containing γ-crystalline and α-crystalline forms. This was followed by another decrease in the overall crystallinity caused by the loading of NMDG, which is dependent on the glucamine density of the final adsorbent. This was evident from the FT-IR spectra (Fig. 7) which showed an enhancement in the amorphous phase of the adsorption band at 1121 cm−1 representing C–C. This trend is likely to be due to the decrease in the overall crystallinity of the glucamine containing fibers.
Furthermore, the bending mode of the CO–NH group at 974 cm−1 corresponds to the characteristics of the crystalline γ-form and its intensity is also reduced with the increase in the density of NMDG in the poly(VBC) grafted nylon-6 fibers to the extent of disappearance at the density of 1.7 mmol g−1-adsorbent. On the other hand, the peak intensity of the CO–NH bending mode at 929 cm−1 associated with the α-crystalline form remains almost unchanged regardless of the density of glucamine in the adsorbent (Fig. 9). These observations confirm that the increase in the amount of glucamine groups loaded into poly(VBC) grafted nylon-6 fibers caused a transition in the crystalline structure from the γ-form to the α-form. The results suggest that the reduction in the overall crystallinity of the glucamine-functionalised fibers is due to the dilution of the crystalline structure with the amorphous NMDG-containing poly(VBC) grafts in the nylon-6 backbones.
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Fig. 9 FT-IR spectra of the original nylon-6, poly(VBC) grafted nylon-6 and glucamine functionalised poly(VBC) grafted nylon-6 with different densities in the range of 810–910 cm−1. |
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Fig. 10 DSC thermograms of the nylon-6, poly(VBC) grafted nylon-6 and glucamine functionalised poly(VBC) grafted nylon-6 fibers with various densities. |
Sample | Glucamine density (mmol g−1 adsorbent) | Tm (°C) | ΔHf (J g−1) |
---|---|---|---|
Nylon-6 | 0.0 | 217.9 | 60.1 |
VBC-grafted nylon-6 | 0.0 | 207.7 | 35.1 |
NMDG functionalised poly(VBC) grafted nylon-6 (1) | 0.5 | 206.9 | 16.8 |
NMDG functionalised poly(VBC) grafted nylon-6 (2) | 1.7 | 208.1 | 15.7 |
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Fig. 11 TGA thermograms of the nylon-6, poly(VBC) grafted nylon-6 fibers and glucamine functionalised poly(VBC) grafted nylon-6 fibers. |
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Fig. 12 The tensile strength and displacement of the original nylon-6, poly(VBC) grafted nylon-6 and glucamine functionalised poly(VBC) grafted nylon-6 fibers. |
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Fig. 13 Effect of pH on boron removal (initial boron concentration 100 mg L−1, adsorbent dose 0.5 g, time 2 hours, temperature 30 °C and stirring speed 200 rpm). |
Fig. 14 shows the variation of the removal efficiency of boron with the fibrous adsorbent dose at two different boron concentrations in boron solution. The removal efficiency increases with the increase in the adsorbent dose from 0.05 to 1.00 g until 100% removal was achieved at 0.5 g and 0.8 g for the treatment of boron solutions having concentrations of 100 mg L−1 and 200 mg L−1, respectively. This observation is due to the increase in the adsorption capacity with the increase in the surface area of the fibrous adsorbent. These results suggest that the new adsorbent is capable of complete removal of boron from solutions and the utilised adsorbent dose depends on the initial concentration of boron in solution. Moreover, it is anticipated that the glucamine-containing poly(VBC) grafted nylon-6 could be an alternative adsorbent for the effective removal of boron from solutions. The most important properties of the glucamine-containing poly(VBC) grafted nylon-6 fibrous adsorbent are presented in Table 7.
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Fig. 14 Effect of adsorbent dosage on boron removal (initial solution concentration 100 and 200 mg L−1, time 2 hours, temperature 30 °C, stirring speed 200 rpm, pH 7). |
Properties | Description |
---|---|
Matrix | Poly(VBC) grafted nylon-6 |
Physical form | Fibers |
Av. fiber diameter | 30 μm |
Chelating group | NMDG |
Glucamine density | 1.70 mmol g−1 |
Adsorption capacity | 13.8 mg g−1 adsorbent (pH = 7) |
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