Optimization Conditions of the Preparation of Activated Carbon Based Egusi ( Cucumeropsis mannii Naudin ) Seed Shells for Nitrate Ions Removal from Wastewater

Egusi seed shells (ESS) were used as precursor for the preparation of two activated carbons (ACs) following H3PO4 and ZnCl2 activation. The effect of factors controlling the preparation of ACs such as chemical activating agent concentration (2 10 M), activation temperature (400 ̊C 700 ̊C) and residence time (30 120 min) were optimized using the Box-Behnken Design (BBD). The optimized activated carbons based H3PO4 (ACP) and ZnCl2 (ACZ) were characterized by N2 adsorption, elemental analysis, atomic force microscopy (AFM), Boehm titration and Fourier transformed infrared (FTIR) techniques. The specific surface area was found to be 1053.91 and 1009.89 m∙g for ACP and ACZ respectively. The adsorbents had similar surface functionalities and were both microporous. The effect of various parameters such as initial pH, concentration, and contact time on the adsorption of nitrate ions on ACP and ACZ in aqueous solution was studied. ACZ demonstrated better adsorption capacity (8.26 mg∙g) compared to ACP (5.65 mg∙g) at the same equilibrium time of 20 min. The adsorption process was governed by a “physical interactions” phenomenon for both adsorbents.


Introduction
The main source of contamination of surface and ground water by nitrate ions is the excessive use of nitrogen fertilizers in agriculture.And the untreated waste water, released from industrial and municipal sites.This increases in disposal of nitrates in the environmental causes, eutrophication of water bodies which stimulates the rapid growth of algae and aquatic plants and consequently, affects fish and other aquatic life negatively [1] [2].The consumption of nitrate contaminated water causes health problems to humans such as methemoglobinemia in infant or baby-blue syndrome and stomach cancer in adults [1] [3].As a result, the World Health Organization (WHO) has fixed a maximum acceptable concentration of nitrate ions in drinking water to be 50 mg•L −1 [4].
Physical, chemical and physicochemical activation are the three common methods used for production of ACs.Physical activation involves two steps: carbonization and activation at high temperature (600˚C -1200˚C) in presence of activating agents such as steam and/or CO 2 [8] [22].Chemical activation is performed in single step, by impregnating the precursor with oxidizing reagents such as KOH, ZnCl 2 , H 3 PO 4 , or K 2 HPO 4 and carbonizing at a lower temperature range (400˚C -700˚C), followed by extensively washing to remove excess activating agent [8] [10] [20].Physicochemical activation is a combination of physical and chemical activation [13] [22].Chemical activation is mostly used because of good yield, and it utilizes less energy and time [19] [23].
Egusi (Cucumeropsis mannii Naudin) is an herbaceous annual plant belonging to the large family of Cucurbitaceae.It is cultivated for seed which is commonly used in food as condiment and thickener (in soup) in Nigeria, Cameroon, Ghana, Middle East, Uganda and other African countries [24] [25] [26].Recently, Giwa et al. [24], show that the oil extract from Egusi seeds could be used as potential feedstock for biodiesel production.To our knowledge, no such study has been done regarding use of Egusi seed shells as a starting material for the preparation of ACs.
In the preparation of ACs by chemical activation, several factors including the carbonization temperature, residential time, impregnation ratio, heating rate influences the properties of the obtained AC.Such multivariate systems, require American Journal of Analytical Chemistry numerous trials to thoroughly investigate the factors which control the system [27] [28].Response Surface Methodology (RSM) is a useful tool; it reduces the number of experimental trials, evaluates the interaction between the studied factors and provide the optimal operating conditions [27] [29] [30].
In present work, we use the Box-Behnken Design (BBD) to optimize the preparation conditions of ACs from ESS by chemical activation using two activating agents (ZnCl 2 and H 3 PO 4 ).The optimized ACs were characterized to determine their specific surface area (N 2 adsorption), surface morphology (Atomic Force Microscopy), elemental analysis, major functional groups (FT-IR spectroscopy and Boehm titration), pH of point of zero charge (pH PZC ), and used as adsorbent for the removal of nitrate ions from aqueous solution.

Preparation of Activated Carbons
The Egusi Seed Shells (ESS) were collected from Mokolo, a local market in the Centre Region of Cameroon.They were washed with deionized water and dried for 24 h at 105˚C.The dried ESS were ground and sieved to 1 -1.25 mm sizes.Impregnation was carried out by adding 50 mL of ZnCl 2 or H 3 PO 4 (2 -10 M) to 10.0 g of ESS and stirred constantly for 12 h at room temperature (27˚C), to ensure completion of reaction between activating agent and ESS particles.This mixture was filtered and the residue was dried in an oven at 105˚C for 24 h [8] [31].The impregnated ESS were carbonized in a muffle furnace (Carbolite Furnaces) at required temperature (400˚C -700˚C), residence time (30 -120 min) and at constant heating rate of 5˚C/min in the absence of oxygen and under self-generated atmosphere.After carbonization, the samples were allowed to cool down to room temperature.The obtained ACs were washed with deionized water repeatedly until the pH of supernatant became neutral and oven dried at 105˚C for 24 h.The samples were then crushed and sieved with an 80 µm diameter mesh sieve and stored in plastic containers.The ACs were labeled as ACZ and ACP for ESS activated with ZnCl 2 and H 3 PO 4 , respectively.

Iodine Number (IN)
The iodine adsorption test is employed to determine the adsorption capacity of AC, and IN value is used to determine if an AC is microporous (0 -2 nm).IN value is obtained as the quantity of Iodine (I 2 ) adsorbed per gram of AC on a milligram scale.The IN for all samples were obtained following ASTM D4907 − 94 method [10] [20].

Methylene Blue Number (MBN)
The MBN is a measure of the mesoporosity (2 -50 nm) of an AC, and is obtained as the amount of dye adsorbed on 1 g of adsorbent [10].The MBN test was performed by mixing 0.020 g of AC and 10 mL of 1000 mg•g −1 MB solution and stirring the solution for 24 h in order to achieve equilibrium state [32].The concentration of MB was measured at 660 nm using a double beam UV-visible spectrophotometer (Thermo Scientific Evolution 300, USA).

Activated Carbon Yield
The activated carbon yield was calculated as the dry weight of obtained AC to raw material according to Equation (1), ( ) where m AC and m 0 are dried mass of AC and the dried mass of raw material respectively.

Experimental Design and Statistical Analysis
The ACs preparation was studied using the Box-Behnken Design (BBD).BBD reduces the number of experiments with no loss of accuracy and estimates complex response functions more effectively, compared to other design [30] [33] [34].Generally, the number of experimental runs is estimated by Equation ( 2) where k and C p are the number of variables studied and the number of central points (replicates) respectively [35].
The three variables studied are the concentration of activating agent (H 3 PO 4 or ZnCl 2 ) (x 1 ), carbonization temperature (x 2 ) and residence time (x 3 ).These variables were chosen based on preliminary studies.The effect of the variables (i.e. x 1 , x 2 , x 3 ) on IN, MBN values and product yield was evaluated using a second order polynomial equation as given by Equation (3) [36].
where, Y is the response obtained, a 0 is a constant, a i slope or linear effect of the input factor x i , a ij , defines a linear interaction between factors x i and x j , a ii is the quadratic effect of factor x i and ε is the random error or represent uncertainties between predicted and measured values.
Minitab16 statistical software (Minitab 16 Inc.) was used for regression analysis of experimental data, to fit the second order polynomials equations and for the evaluation of the statistical significance of the developed equations (Equation ( 3)).The response surface plots were generated using SigmaPlot 11 software (Systat.Software, Inc.) to study the relationship between the factors and the responses.The surface functional groups of ACs was determined by both Boehm titration method [37] and FT-IR spectroscopy (Brucker Vector-22, Germany) using KBr pellets in transmission mode within the 400 -4000 cm −1 range.The pH of point of zero charge (pH PZC ) was determined by the drift method [2].

Adsorption Studies of Nitrate Ions
Adsorption studies were conducted in order to investigate the effects of pH, adsorbate concentration and contact time on the adsorption of   [38].The adsorbed quantity at equilibrium q e (mg•g −1 ) was calculated from Equation ( 4) where, C 0 and C e (mg•L −1 ) are the concentration of and ACZ.The non-linear form of these isotherm models is given in Table 1.
The effect of pH (3 -11) on the adsorption of 3 NO − by both ACP and ACZ was conducted using pH meter (Insmark, model IS 128).pH of solution was adjusted by adding 0.1 M NaOH or 0.1 M HCl solutions.The concentration of 3 NO − and adsorbent (ACP and ACZ) dose used were 50 mg•L −1 and 0.1 g, re- spectively.
For kinetics studies, batch adsorption experiments were carried out by stirring 0.1 g of adsorbent (ACP and ACP) and 100 ml of where, C 0 and C t (mg•L −1 ) are the initial and at time t concentration of The kinetic models: pseudo-first-order, pseudo-second-order and intraparticle diffusion is given in Table 1.
Table 1.Different isotherm and kinetic models.

Non-linear equation Parameters
Freundlich : adsorbed quantity at time t t (min): contact time k 1 (min −1 ): pseudo-fist order rate constant Pseudo-second-order , where, q e.exp and q e.pre are experimental and predicted equilibrium adsorption capacities.

Proximate and Elemental Analyses of ESS
The data collected for the proximate and elemental analyses of Egusi seed shell (ESS) are given in Table 2.For comparative purposes, data from other precursors are also provided.The ESS contains 6.32% moisture, 69.53% volatile matter, 4.13% ash content and 20.02% fixed carbon.The elemental analysis shows that ESS is American Journal of Analytical Chemistry mainly composed of carbon (47.02%), hydrogen (5.46%), nitrogen (3.16%) and oxygen (44.36%).The amount of nitrogen in ESS is comparatively higher than previously used precursors, while other compositions are nearly same.Being studied for the first time, the ESS precursor has a low ash and high carbon content and is therefore an appropriate raw material for ACs production.

TGA Analysis of ESS
The carbonization temperature of ACs production depends on the thermal behavior of precursor (ESS), therefore, ESS was subjected to thermogravimetric analysis (TGA), TGA profile is given in Figure 1.TGA suggests three stages of weight loss during pyrolysis.The first stage shows 9.98% weight loss in the temperature range of 27˚C -160˚C, quite possibly due to removal of surface bound water and moisture.The second stage, characterized by a weight loss of 52.34%, from 160˚C to 400˚C, could be due to the decomposition of cellulose, hemicellulose  and few lignin [20] [39].In final stage of pyrolysis, 400˚C and above (gradually and continuously up to 900˚C), the weight loss (16.80%) corresponds to the decomposition of lignin and formation of carbon material.The residue was about 22.38%.Hence, the temperature range of 400˚C to 700˚C was considered as the carbonization temperature in this study.

FTIR Analysis of ESS
The FTIR spectrum of ESS is presented in Figure 2. The broad peak appearing at 3389.6 cm −1 is attributed to the O-H bond stretching vibration of water, cellulose, hemicellulose and lignin (main constituent of ESS) [18].The two peaks at 2928.

Design of Experiments Using Box-Behnken Design
The  3. Experiments 13 to 15 were performed when all the studied parameters were at the center of the studied domain in order to determine the experimental error and the reproducibility of data.

Iodine Absorption
The results obtained from Iodine adsorption are given in   4).Two quadratic regression models were used to predict the optimal IN value of ACP (Y 1 ) and ACZ (Y 4 ) (Equations ( 9) and ( 12)) respectively).By applying the statistical model ANOVA, (see Table 4), it is clearly seen that the experimental and predicted values are in good agreement, since the correlation coefficient of the model is close to unity for both ACs (R 2 = 0.93 and 0.91 for ACP and ACZ respectively).The significant terms are x 2 and 2 1 x for ACP, and x 1 , x 2 and 2 1 x for ACZ, given that the p-value of these terms are less than 0.05.It is also noted that IN values are significantly affected by the concentration of activating agent (x 1 ) and carbonization temperature (x 2 ), while the effect of residence time (x 3 ) is insignificant.Figure 3  tivating agent increase, the interaction between activating agents and raw material increases and generating porosity [31].When the concentration of activating agent is too high, two possibilities occur: 1) new micropores do not form, while existing ones are continuously enlarged [31] and 2), the excess and/or unreacted activating agent blocks the pores [41] resulting to a decrease in microporosity, which is directly link to the Iodine absorption capacity.

Lower concentration of activating agent resulted to lower IN values, probably
due to incomplete reaction between activating agent and the raw material.

Methylene Blue Absorption
For the methylene blue adsorption, the values of MBN varied from 107.05 to 374.14 mg•g −1 for ACP and 149.88 to 374.25 mg•g −1 for ACZ (see Table 3).In both ACs, the MBN was significantly influenced by the concentration of activating agent (x 1 ) and activation temperature (x 2 ), see Table 4.For the prediction of MB adsorption capacity, quadratic regression model Equations (( 11) and ( 12)) were used for ACP (Y 2 ) and ACZ (Y 5 ), respectively.
The correlation coefficients (R 2 ) were found to be 0.94 and 0.93 respectively (see Table 4), which indicate good fitting of the described models.The significant terms of the selected models given in Table 4 are x 1 , x 2 , 2 1 x and 2 3 x (p-values are less than 0.05).Figure 4 depicts the response surface plots based on the interactions and effect of concentration (x 1 ) and temperature (x 2 ) on methylene blue adsorption value.The residence time was kept fixed at the center point for all plots.The value of MBN increases as a function of two significant variables (concentration and temperature) for both ACP and ACZ.The observed results are in agreement with that reported by Tan et al. [9], who indicated that the impregnation ratio and temperature have significant effect on the pore size and structure of AC from mango stem peel using KOH as activating agent.Similarly, Kouotou et al. [13] using H 3 PO 4 and Sayğili and Güzel [18] using ZnCl 2 , found well-developed mesopores of ACs with increasing value of studied factors (i.e.concentration and temperature).The increase in MBN value with the concentration and temperature, was also considered to be due to the depolymerization of cellulose and distillation of tar from the carbon at high temperatures (above 500˚C), which generate more mesopores in the resultant ACs [40].

Activated Carbon Yield
The resultant yield of ACs is a key response factor directed to production.A set of experiment were performed with variable experimental conditions, in order to determine the optimal conditions for obtaining maximum yield of product (i.e. ACP and ACZ).According to the results (Table 3), the maximum yield of ACP and ACZ was achieved at low concentration of activating agent with least carbonization time, (experiment 1), whereas, minimum yield was obtained at high temperature and longer residence time (experiment 12).The ACP yield was in the range 27.31% -52.25% and similar to the ACZ yield (26.60% -49.93%).The results of ANOVA for the response of ACP yield (Y 3 ) and ACZ yield (Y 6 ) (Equations ( 13) and ( 14)) and their correlation coefficients are given in Table 4.
All the terms, x 2 , x 3 , x 1 x 2 and x 1 x 3 and x 1 , x 3 , x 1 x 2 for ACP and ACZ respectively (see Table 4) are significant.Figure 5 illustrates the response surface graph of carbonization temperature (x 2 ) and residential time (x 3 ) against the obtained yield.The concentration was maintained at the center point (6 M).It is observed from the graph that an increase in activation temperature leads to a decrease in the obtainable yield, whereas, residence time does not significantly affect the response.This decrease in yield may be attributed to the fact that an increase in activation temperature increases the quantity of carbon burn-off and the continuous liberation of the volatile matter which is reflected as a loss of adsorbent Figure 5. Response surface plot for the effect of temperature and time on yield of (a) ACP, (b) ACZ.American Journal of Analytical Chemistry material.The maximum yield was achieved when the temperature and residence time were maintained at their lowest value and the concentration was kept constant at the central point.The obtained results are in accordance with those from the literature [9] [20] [23] and it can therefore be concluded that, the activation temperature has a greater impact compared to the residence time on the AC yield.

Optimization Process and Validation Test
The optimization process and method validation are quite essential in setting up the optimum conditions for maximum AC yield, high iodine and methylene blue adsorption capacity from the precursor.However, it is difficult to optimize these three responses under the same conditions because the zone of interest of the factors is different.The desirability function was then applied using Minitab

Specific Surface Area
The surface area of ACs was determinate through multipoint BET method by keeping the relative pressure (P/P 0 ) in the range of 0.02 to 0.3.The pore size parameters were calculated using Dubinin-Astakhov method.The results are summarized in Table 6.The linear plot of the multipoint BET (Figure 6) gave a surface area (S BET ) of 1058.91 m 2 •g −1 and 1008.99 m 2 •g −1 for ACP and ACZ respectively.The total pore volume was found to be 0.663 and 0.594 cm 3 .g−1 , and the average pore size of ACP and ACZ were obtained as 1.84 and 2.02 nm respectively.The average pore size indicates that the prepared ACs are microporous according to IUPAC classification [14].Hence, both ACs show similar characteristic even though prepared at different carbonization temperature and concentration of activating agent.

Surface Morphology
The surface morphology of the precursor (Figure 7

Determination of Surface Functional Groups
The optimized ACs were subjected to Boehm's titration and FTIR spectroscopy in order to determine the surface functional groups.The results from Boehm's titration show that ACP and ACZ contain higher number of acidic groups (Table 6).The basicity character in ACP is comparatively weaker (0.43 mmol.g −1 ) than that for ACZ (0.93 mmol.g −1 ).The pH of point of zero charge, pH PZC was found to be 4.00 and 7.02 for ACP and ACZ respectively.
The FTIR spectra of the ACs are noticeably different from that of the precursor American Journal of Analytical Chemistry (see Figure 2).After activation and carbonization, there is the disappearance of some peaks in the FTIR spectra of the ACs and considerable decrease in the intensity of some peaks due to decomposition of cellulose, hemicellulose and lignin during the carbonization process [43].However, there is an outstanding similarity in the spectra of both ACs.The band at 3421.

Elemental Analysis
The results of the elemental analysis are provided in Table 6.The carbon content of ACP and ACZ are significantly higher compared to that of the precursor (47.02%).This could be due to an increase in the degree of aromaticity [15].A decrease in the quantity of non-carbon species such as hydrogen, nitrogen and oxygen was observed, probably due to the release of moisture and volatile substances during carbonization process [17].The difference in elemental analysis between ACP and ACZ could be explained by the relative low concentration of activating reagent and carbonization temperature involve in the preparation of ACP (Table 5).

Effect of Initial pH
An initial nitrate ions concentration of 50 mg•L −1 was used to study the effect of pH on removal of nitrate ions in the range of 3 -11.The maximum quantity of nitrate ion removed occurred at pH 3, and this amount decreases with increase in pH (Figure 8).The surface of ACs at low pH (pH ˂ pH PZC ) is predominantly positively charged as a result of the protonation of surface functional group(s), hence, more adsorption of nitrate ions by electrostatic attraction [42].An increase in pH causes reduction of number of positive sites on the surface of the adsorbents, resulting to a reduction of adsorption capacity of adsorbent toward nitrate ions.

Effect of Initial Concentration and Equilibrium Adsorption Isotherms
The experimental data obtained was analyzed using Freundlich, Langmuir, D-K and Tempkin non-linear isotherm models (see Figure 9).The best fit of the experimental data was analyzed based on R 2 , RMSE and χ 2 .Hence, high R 2 value, low RMSE and χ 2 value established the best fitting adsorption isotherm [6].American Journal of Analytical Chemistry  According to the presented result in Table 7, some discrepancies were observed in the Langmuir isotherm adsorption; lowest R 2 values, high RMSE and χ 2 values, unreasonably large value of Q m and insignificant K L , rendering this model unsuitable to explain the adsorption phenomenon on ACP and ACZ.The Freundlich and D-K isotherms both fit the experimental data.In addition, the n values obtained from the Freundlich adsorption isotherm model were 0.687 and 0.730 for ACP and ACZ, respectively.These values indicate that physisorption is dominant the process for both adsorbents [6].The energy associated with the adsorption process can be calculated from the D-K model using the equation below ( ) From the model, if the magnitude of the energy (E) lies in the range of 8 -16 kJ•mol −1 , the sorption process is said to take place via ion exchange, whereas, if E < 8 kJ•mol −1 , the sorption process is said to be controlled by physical adsorption.
The values of E were found to be 0.021 and 0.027 kJ•mol −1 for ACP and ACZ, respectively, implying physical adsorption is dominant [2].

Effect of Contact Time and Kinetic Studies
The adsorption process was analyzed using three kinetic models, pseudo-first-order, pseudo-second-order and intraparticle diffusion kinetic model.rate-controlling step.In addition, the value of C i ≠ 0, suggest the adsorption is a complex process and involve more than one diffusive resistance process [5].

Conclusion
In

3 NO 3 NO
− on ACP and ACZ.All experiments were performed repeatedly to get statistical value.For equilibrium adsorption studies, a set of Erlenmeyer flasks containing 100 mL − solution in the concentration range of 20 to 200 mg•L −1 and 0.

3 NO−
at initial and equili- brium state respectively; V (L) is the volume of solution; and m (g) the mass of the dry adsorbent.Three isotherm models, Freundlich, Langmuir and Dubinin-Radushkevich (D-R) were used to study the nitrate ions adsorption on ACP

3 NOThe residual concentration of 3 NO 3 NO
− solution (50 mg•L −1 ).− in solution was determined at different time interval in range of 5 -90 min.The quantity of − adsorbed was calcu- lated by the following Equation(5) 1/n : Freundlich adsorption constant n (dimensionless): empirical parameter representing the energetic heterogeneity of surface q e (mg•g −1 ): equilibrium adsorbed quantity Langmuir 1
3 and 2862.7 cm −1 are due to symmetric and asymmetric stretching vibration of methyl group, and the peak at 1737.6 cm −1 indicates the stretching vibration of carbonyl group (C=O) of hemicellulose and lignin[18].The bands found in the 1653.4-1515.6 cm −1 range are responsible for N-H bond stretching.More vibrations were observed between 1459 and 1377.3 cm −1 can be ascribed to aliphatic and aromatic C-H groups in the plane deformation vibration.The bands between of 1261.0 -1041.7 cm −1 could be assigned to the C-O stretching vibration of carboxylic acid and alcohols[18].
Iodine Number (IN), Methylene Blue Number (MBN) and ACs yield were chosen as responses for the Box-Behnken design.The experimental matrix, together with the experimental and predicted values of the responses are given in Table illustrates the response surface plots, obtained by plotting temperature and concentration against IN values, with the residence time kept constant at the center point (75 min).A consistent trend was observed in ACP and ACZ; the IN value increases as the temperature increases.This may be explained by considering that at higher temperatures, there is a greater chance of volatile matter to vaporize from the precursor, causing an increase in pore development and/or formation of new micropores (or active sites)[12] [40], hence an increase in the IN value.Tounsadi et al. (2016)[10] reported similar results.Furthermore, an increase in concentration of activating agent leads to an increase up to a maximum of 6 M for ACP (Figure3(a)) and 8 M for ACZ (Figure 3(b)) of the IN value.Any further increase in the concentration of activating agents, causes a decrease in the IN value.As the concentration of ac-

Figure 3 .
Figure 3. Response surface plot for the effect of temperature and concentration on IN value of (a) ACP, (b) ACZ.

Figure 4 .
Figure 4. Response surface plot for the effect of temperature and concentration on MBN value of (a) ACP, (b) ACZ.
16 software in order to consolidate the three factors by considering the same weight for all the factors on the three responses[13] [29].The results of this optimization are presented in Table5.The experimental responses are close to the predicted value, there was no significant difference between predicted and experimental data.A residence time of 30 min led to maximum yield irrespective of the activating agent.The optimum conditions for ACP are H 3 PO 4 concentration of 7 M at a carbonization temperature of 633˚C, and ZnCl 2 concentration of 10 M and carbonization temperature of 698˚C for ACZ.These results show that, the AC obtained through H 3 PO 4 activation require less concentration at comparative low temperature compared to that obtained from ZnCl 2 .

Figure 6 .
Figure 6.BET specific surface area plots of ACP and ACZ.
(a)), ACP (Figure 7(b)) and ACZ (Figure 7(c)) was assessed by AFM.The images show the presence of well-developed pores and cavities on the surface of ACP and ACZ, and no or undeveloped pores on the precursor's surface.Therefore, surface modification and pore development occurs during activation and carbonization process [42].
6 cm −1 is attributed to the O-H bond stretching vibration of absorbed water molecules[2].The weak bands at 2923.6 and 2853.4 cm −1 indicate the C-H stretching vibration of methyl and methylene group(s)[31] [43], while the two bands appearing at 1743.9 and 1701.0 cm −1 are attributed to the carbonyl group (C=O) of esters and carboxylic acid respectively[12].The presence of C=C of aromatic ring stretching vibration is recognized by the band observed at 1541.4 cm −1 .The bands between 1400 and 1070.6 cm −1 signifies the presence of primary, secondary and ternary alcohol, phenol, ether and esters showing C-O stretching and O-H bond deformation vibration[31].The peak at 673.6 cm −1 is indicates the out-of-plane O-H vibration[15] [44].

Figure 8 .
Figure 8.Effect of pH on the adsorption of

Figure 9 .
Figure 9. Adsorption isotherms of the present study, Box-Behnken design was used to optimize the preparation conditions of ACs from Egusi seed shells (Cucumeropsis mannii) by chemical activation using two activating agents (H 3 PO 4 and ZnCl 2 ).The ability of the optimized ACs (ACP and ACZ) towards nitrate ions removal was investigated.During optimization, the residence time for maximal responses (IN, MBN, and obtained yield) was 30 minutes for both ACP and ACZ.The concentration of H 3 PO 4 and ZnCl 2 and the carbonization temperature was 7 M at 633˚C and 10 M at 698˚C for ACP and ACZ respectively.ACP and ACZ were found to be microporous having surface areas of 1053.91 m 2 •g −1 and 1009.89m 2 •g −1 respectively, obtained from BET analysis.FTIR showed that both ACs have approximately same surface chemistry.AFM images show the presence of well-developed pores and cavities on the surface of ACP and ACZ, which were absent in the precursor material.Maximum adsorption occurs at pH 3 and the adsorption equilibrium was reached after 20 minutes for both ACs.ACZ showed a better adsorption capacity of nitrate ion as compared to ACP.The equilibrium and kinetic studies reveal that physical interaction exhibits between adsorbent and adsorbate.This study demonstrates the potential of Egusi seed shell as a good precursor for the

Table 2 .
Proximate and ultimate analyses of Egusi seed shells.
b no detection; a by difference.

Table 3 .
Experimental design matrix for optimization using BBD.

Table 4 .
Analysis of variance (ANOVA) for the regression model for IN, MBN and ACs Yield.

Table 6 .
Chemical, physical and textural characteristics of ACs.no detection; c pH of point of zero charge.
a calculated by difference; b

Table 7 .
Adsorption isotherm parameters for the adsorption of 3NO − on ACP and ACZ.

Table 8 .
Kinetics constants for the adsorption of 3 NO − on ACP and ACZ.