Natural coagulants from plants resources have gained a lot of attention as it is renewable, biodegradable, non-hazardous, lower cost, and less sludge generated compared to chemical coagulants. However there are still some drawbacks, namely long settling time and possible increase of dissolved organic carbon in the treated water. In this paper we tried to address these drawbacks by utilizing citrate modified Fe3O4 to adsorb protein from Leucaena leucocephala as the active coagulating agent. The effect of trisodium citrate concentration and protein adsorption pH to the adsorbed protein was investigated. It was found that the trisodium citrate concentration of 0.5 M and pH 4.0 gave the highest protein adsorption. The obtained magnetic coagulant was furthermore characterized using Scanning Electron Microscopy, X-ray Diffraction, Fourier Transform Infrared Spectroscopy, and Transmission Electron Microscopy to observe the characteristics before and after protein adsorption. Furthermore, the effect of pH (2 to 10) and coagulant dosage (60 to 600 mg L-1) to the removal of synthetic Congo red wastewater and sludge volume formation was investigated. It was found that pH 3 was the best pH for coagulation due to charge neutralization mechanism of leucaena protein. Furthermore the highest removal was obtained at dosage 420 mg L-1 with 80% removal. This result was comparable with crude extract of leucaena with half settling time (20 min) and lower increase of permanganate value, indicating lower increase of dissolved organics in the treated water.
Research
Adsorbed leucaena protein on citrate modified Fe3O4 nanoparticles: synthesis, characterization, and its application as magnetic coagulant
https://doi.org/10.21203/rs.3.rs-41412/v4
This work is licensed under a CC BY 4.0 License
Journal Publication
published 11 Dec, 2020
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Congo red
Fe3O4
iron oxide nanoparticles
Leucaena leucocephala
magnetic coagulant
natural coagulant
In recent years, utilization of various natural resources as natural coagulant has gained a lot of interest due to its various advantages, such as: lower cost compared to chemical coagulants, it comes from renewable sources, less sludge volume generated, and biodegradable- non-hazardous sludge [1, 2]. However there are some drawbacks in natural coagulant application, which we addressed in this research. Firstly, the settling time needed for separation of flocs is most likely between 60 to 120 min by gravity. It is important to decrease the settling time, as long residence time could lead to larger designed settling tank needed, which could lead to higher capital cost. Secondly, direct utilization of plant parts or its crude extract could increase the dissolved organic carbon (DOC) in the treated water, due to some soluble non-coagulant compounds from the plant [3]. It is known that high DOC could stimulate high microbial activities, making disinfection process more difficult.
There were some researchers that combined iron oxide nanoparticles and natural coagulant to improve the coagulation performance, especially in terms of settling time [4-10]. There are two approaches that have been used, firstly the protein as active coagulating agent was used to functionalize the surface of iron oxide nanoparticles, secondly, the iron oxide nanoparticles were dispersed in crude extract of natural coagulant. Okoli et al. [4] synthesized magnetic coagulant using composite of Fe3O4 and γ-Fe2O3 water-oil emulsion and functionalized with purified protein from Moringa oleifera. It was reported that 90% turbidity removal was obtained at 12 min settling under external magnet force, compared to gravitation only (240 min).
Different types of iron oxide nanoparticles, α-Fe2O3, γ-Fe2O3, and Fe3O4, have been studied by Santos group to remove turbidity and color from synthetic wastewater [5-9]. In those researches, iron oxide nanoparticles were dispersed in crude extract of M. oleifera, where it was found that significant removal of turbidity and color was achieved within short settling time (less than 30 min) under magnetic settling. It was also found that the coagulation mechanism was mostly charge neutralization, where protein acted as the active coagulating agent, and interaction between protein and iron oxide nanoparticles made the fast settling process possible. Similar result was also obtained in our previous study [10] where magnetically assisted coagulation of Congo red gave half settling time when compared to leucaena extract only with similar removal value. Vieira group isolated globulin and albumin fraction from M. oleifera and functionalized it with iron oxide nanoparticles [11, 12]. The obtained magnetic coagulant was used to remove color from synthetic dye waste namely Amaranth, Brilliant Blue, Sunset Yellow, and Reactive Black 5. Combination of albumin and iron oxide nanoparticles gave color removal around 52-94%, depending to the dyes, with 5 min magnetic sedimentation.
Concerning the high DOC content of natural coagulant treated water; some efforts have been done by previous researchers. Yin [1] suggested that extraction and isolation of active coagulating agent could tackle this problem. Extraction of active coagulating agent, especially protein, using saline has been extensively studied. It has been proven that salting-in interaction between NaCl and protein could increase the protein solubility, resulting in lower dosage needed in the coagulation. This extraction step could be followed by purification steps to isolate protein that acts as active coagulating agent. Several purification methods have been investigated, such as ion exchange [13-15], dialysis [16], spray drying [17], ultrafiltration [18, 19], and lyophilization [20]. However, the previously mentioned methods require many complicated steps, making it impractical in large scale.
Iron oxide nanoparticles are known to be able to selectively bind protein thus could be used in protein purification [21]. However, for its application in aqueous medium, the hydrophobicity of iron oxide nanoparticles becomes its drawback [22]. On the other hand, the presence of hydroxyl group on the surface of iron oxide nanoparticles makes the surface of particles easily modified using various functional groups, one of which is carboxylic acid [23]. Citric acid, a trivalent organic acid, has been widely used as capping agent to prevent agglomeration of iron nanoparticles. Furthermore, citric acid modified iron oxide nanoparticles has shown affinity for immobilize protein, enzymes, drugs, etc. [24-29].
In this study, we investigate functionalized Fe3O4 nanoparticles with protein from leucaena (Leucaena leucocephala) crude extract as magnetic natural coagulant to treat synthetic Congo red wastewater. To the best of authors’ knowledge, this study is the first study that reported utilization of adsorbed protein on citrate modified Fe3O4 as magnetic coagulant. Based on our previous study, leucaena protein could act as natural coagulant to remove turbidity [30] and color [31]. The Fe3O4 was modified using citrate ion that acted as a bridge for protein adsorption. The effect of pH modification and citrate ion concentration to the protein adsorbed was investigated. The best condition that gave the highest adsorbed protein was characterized and used as magnetic coagulant for Congo red removal from synthetic wastewater. The effects of coagulation pH, magnetic coagulant dosage, and removal kinetics under magnetic field were investigated. Furthermore, the changes of DOC in the wastewater before and after coagulation using magnetic coagulant and crude extract were estimated using permanganate value (PV).
2.1. Synthesis of magnetic coagulant
The synthesis of magnetic coagulant was following the method used by Rahman et al. [27] with modification. A mixture of 80 mg Fe3O4 (pure grade, Sigma Aldrich) and 160 mL trisodium citrate (pure grade, Sigma Aldrich) was sonicated for 30 min, followed by mixing for 2 h at 80 °C. The mixture was let cool to room temperature, then separated using magnet, and washed using distilled water to remove unadsorbed citrate anion. The citrate modified Fe3O4, denoted as Fe3O4-CA, was then oven dried in vacuum condition at 60 °C, and then stored in a closed lid in a desiccator.
Leucaena protein was used as the protein source to functionalize the Fe3O4-CA. Dried leucaena seeds were obtained from Probolinggo, East Java. The seeds kernel was separated from its coat by grinding and sieving. Furthermore, the seeds kernel was grinded and sieved using a standard mesh to obtain seeds kernel powder with size smaller than 0.177 mm (80 mesh). Extraction of protein from seeds kernel powder was done by using 1 M NaCl solution with seeds to solvent mass ratio of 1:20 using dispersed batch method for 60 min. The cake was separated by mean of filtration, and the extract was used for Fe3O4-CA functionalization. To prevent any degradation during storage, the extract was freshly made prior to every experiment. Observation of leucaena isoelectric point (pI) was done by similar extraction procedure with variations of initial pH (2 to 9), adjusted using 0.1 M HCl or NaOH solution. The extracted protein concentration in the solution was determined using Bradford method [32].
Functionalization of Fe3O4-CA was done by mixing 5 mL of leucaena crude extract, in which pH was adjusted using 0.1 M citrate buffer solution, prior to mixing with 80 mg Fe3O4-CA. The mixture was sonicated for 1 min, followed by mixing at room temperature for 4 h. The protein functionalized iron nanoparticles, denoted as Fe3O4-CA-protein, was separated using external magnet, washed with distilled water, and vacuum dried at 60 °C. The obtained Fe3O4-CA-protein was stored in a closed lid in a desiccator.
The functionalization of Fe3O4-CA was first done at various pH (3 to 6) at constant trisodium citrate concentration of 0.5 M to observe the effect of pH to the protein adsorption. Furthermore, the effect of trisodium citrate concentration was studied at the best pH by varying trisodium citrate concentration (0 to 1.0 M). The protein concentration in the solution before and after adsorption was determined using Bradford method [32], where the protein concentration was stated equivalent to bovine serum albumin (BSA) standard. The response observed was the protein adsorption capacity (q; mg eq BSA mg-1 Fe3O4), which was calculated using Eq. (1), where Ct and Ce (mg eq BSA L-1) were initial and final protein concentration, m (mg) is the mass of Fe3O4, and V (L) is the volume of the solution. The obtained Fe3O4-CA-protein with highest protein adsorption capacity was further characterized and used as magnetic coagulant in this study.
2.2. Characterization
The magnetic coagulant that gave the highest protein adsorption was characterized to observe the difference before and after protein functionalization. Determination of point of zero charge (pHpzc) of pristine and citrate modified Fe3O4 was done using pH drift method [33]. The functional groups of pristine Fe3O4, citrate modified Fe3O4, and protein functionalized Fe3O4 were characterized using KBr pellet method Fourier Transform Infrared Spectroscopy (FTIR; Prestige 21 Shimadzu Instruments). The morphology was observed using Scanning Electron Microscope (SEM; Hitachi SU3500). The particle size was observed using Transmission Electron Microscope (TEM; Hitachi HT7700), while the crystallinity was analyzed using X-Ray Diffraction (XRD; Bruker D8 Advance). Based on the XRD spectra, the crystallite size (d in nm) was estimated using Scherrer equation (Eq. (2)), where θ is the Bragg angle; K is Scherrer constant (0.9); λ (nm) is the wavelength of Cu K-α radiation (0.15405 nm); and β is the full width at half maximum peak.
2.3. Jar test experiment
The obtained magnetic coagulant was tested to remove synthetic dye wastewater. Congo red (Aldrich) dissolved in distilled water with concentration of 10 ppm was used as the model dye in this study. Coagulation study was done by mixing magnetic coagulant and Congo red solution with rapid mixing at 100 rpm for 2 min, followed by slow mixing at 20 rpm for 20 min using a jar test apparatus. The mixture was then let to settle in an Imhoff cone under array of neodymium magnets. During this step, sample of treated water was taken every 5 min until 1 h. The concentration of Congo red at initial condition and during sampling was measured using a spectrophotometer at its maximum wavelength (505 nm). The removal of Congo red was calculated using Eq. (3), where Ai and At are initial and final absorbance, respectively. The sludge volume (mL L-1) was measured using Imhoff cone after 1 h settling, and calculated using Eq. (4). The effect of pH to the coagulation was observed by varying the wastewater pH (2 to 10) at constant dosage of 60 mg L-1. Furthermore, the study of magnetic coagulant dosage’s effect to coagulation was done at best pH at various coagulant dosages (60 to 600 mg L-1).
The PV was measured at the best pH and coagulant dosage using following method [34]: 5 mL of 4 N H2SO4 and 10 mL of 0.1 N KMnO4 were added into 100 mL of sample solution. The mixture was heated for 10 min, after which 10 mL of 0.01 N H2C2O4 solutions was added. The solution is back titrated using KMnO4 solution until the end point was reached. The volume titration of the potassium permanganate solution used was recorded, and the PV (mg KMnO4 L-1) was calculated.
2.4. Settling kinetic models
The evaluation of removal during settling was approached using several adsorption kinetic models. The value of adsorption capacity, q (mg dye mg magnetic coagulant-1), was calculated using Eq. (1).
The kinetic models used in this study are pseudo-first order, pseudo-second order, Elovich, and intra-particle diffusion models, where the linearized form for each model is presented in Eqs. (5) to (8) [35], respectively. The qt and qe values in those equations represent adsorption capacity (mg dye g-1 magnetic coagulant) as function of time (min) and at equilibrium. Constant k1 (min-1) represents pseudo first-order rate constant; k2 (mg dye g-1 magnetic coagulant min-1) is the pseudo second-order rate constant; and kd (mg dye g-1 magnetic coagulant min-1/2) is the rate constant for intra-particle diffusion model. The value α denotes initial adsorption rate (mg dye g-1 magnetic coagulant min-1) and β (mg magnetic coagulant g-1 dye) is the activation energy related value of chemisorption for Elovich model.
3.1. Effect of pH and trisodium citrate concentration on the protein adsorption
As mentioned before, the citrate ion was used as a bridge between Fe3O4 and leucaena protein, making the adsorption process effectively. The effect of adsorption pH and trisodium citrate concentration is presented in Figs. 1a and 1b. It could be observed in Fig. 1a, that pH played an important role in protein adsorption. With the increase of adsorption pH from 3.0 to 4.0, the leucaena protein adsorption capacity was also increased and reached the highest adsorption capacity at pH 4.0. Further increase of adsorption pH to 6.0 led to the decrease of protein adsorption. It is known that electrostatic force plays an important role in protein adsorption. From the pHpzc (Fig. 1c), it could be observed that citrate modified Fe3O4 had lower pI (around 3.9), compared to the pristine one (around 7.1). This result is consistent with previous research [36]. On the other hand, the leucaena protein’s pI was estimated around pH 4 (Fig. 1d), where the protein solubility is at its minimum [37]. At low pH, both Fe3O4 and leucaena protein had positive charges, thus repulsive forces between them making low adsorption. Similar phenomenon was possibly happened at pH above 4.0. The highest protein adsorption capacity was obtained at pH 4.0, which was near pI of leucaena protein. It is known that at pH near pI, the protein structure is at more compact conformation state, lowering repulsion forces between particles thus making higher protein adsorption possible [38]. Similar phenomenon has also been reported before [38, 39].
The effect of trisodium citrate concentration to the protein adsorption was further investigated. It was found that addition of trisodium citrate could increase the protein adsorption capacity. Based on Fig. 1b, it could be observed that the addition of trisodium citrate to 0.5 M increased the protein adsorption. We speculate it is possible due to with increase of citrate ion in the modification process, more citrate ions are adsorbed on Fe3O4 surface, making more protein adsorption possible. Further addition of citrate ion did not increase the adsorption capacity, due to all Fe3O4 surface already occupied. Similar result was also obtained by previous researchers [27]. Based on these results, the trisodium citrate of 0.5 M and protein adsorption at pH 4.0 were further characterized and used as magnetic coagulant.
3.2. Characterization of Fe-CA-Protein
The characteristics of Fe3O4 before and after protein modification are presented in Fig. 2. Based on the SEM observation, the nanoparticles were in form of aggregation of Fe3O4. The functionalization did not give any significant difference to the particle morphology. Similar spectra were also observed for Fe3O4 and Fe3O4-CA-protein samples, where both samples exhibited (111), (202), (311), (222), (400), (422), (511), and (440) peaks of magnetite [40]. Further calculation using Scherer equation showed that functionalized Fe3O4 had bigger average diameter of 58 nm, compared to pristine Fe3O4 (47 nm). Based on the Fe3O4 IR spectra, it could be observed that the sample exhibited a Fe-O vibration at 580 cm-1, and peaks at 1613, 3436 cm-1 that came from O-H vibration of water molecule on the crystal structure [41, 42]. After modification using CA, the Fe3O4-CA sample exhibited stronger peak at 1620 and 3436 cm-1 indicating symmetric stretching of C=O and O-H vibration from CA molecules that adsorbed on the surface of Fe3O4. After adsorption of protein, there are several peaks that could be observed: 1397 cm-1 bending vibration of C-H bonds, ~1600 cm-1 peak of N-H bending, while peaks around 3200-3400 cm-1 came from overlap of O-H and N-H stretching [27, 43]. The observed peaks indicated that protein from leucaena crude extract has been adsorbed on the surface of modified Fe3O4. The presence of coating of protein on Fe3O4 was visible in TEM image (Fig. 2f, white arrow), compared to pristine Fe3O4.
3.3. Effect of pH in coagulation
The effect of pH in the coagulation process is presented in Fig. 3. It could be observed that there was increase of removal from pH 2 to 3, and the highest removal of Congo red was obtained at pH 3. Very low removal was obtained while increasing the pH from 4 to 10, indicating no coagulation process happened. The leucaena protein on magnetic coagulant possessed pI around 4, thus at pH below 4, the magnetic coagulant would be positively charged. This charge was the opposite of Congo red molecules, which is known to be negatively charged at pH ≥ 3, making the coagulation process possible through charge neutralization mechanism. At pH 2, low coagulation performance was due to denaturation of protein molecules on the magnetic coagulant. Denaturation of protein is commonly observed at extremely low pH [44], making it inactive for coagulation process. On the other hand, at pH above leucaena protein pI value, both the coagulant and Congo red molecules were positively charge, thus no coagulation occurred at these conditions. Along with the increase of destabilized Congo red molecules, the more sludge volume was generated, as observed in pH 3. As very low removal was observed at pH 4-10, minimum destabilization was occurred, resulting in no observed sludge. Similar result was obtained in our previous studies using leucaena crude extract as natural coagulant, where pH 3 was the best pH for coagulation [10, 31].
3.4. Effect of magnetic coagulant dosage
The study of magnetic coagulant dosage was done at pH 3, which was found as the best pH for coagulation. The profile of % removal and sludge volume at various dosages is presented in Fig. 4. At low coagulant dosage, there was insufficient coagulant to neutralize the Congo red molecules, resulting on low removal. With increase of magnetic coagulant dosage, the removal was also increased until dosage of 420 mg L-1. Further increase of magnetic coagulant dosage to 600 mg L-1 did not give any significant increase to the removal of Congo red. This was possible due to over addition of coagulant limiting the adsorption efficiency, as the magnetic coagulant particle could aggregate to each other [45] lowering the coagulation efficiency. Furthermore colloid re-stabilization is known to be commonly happened under over addition of coagulant [46]. This phenomenon could decrease the removal efficiency. Similar trend was also observed for the sludge volume.
The Congo red removal as function of time is presented in Fig. 5. Comparison experiments were done using only leucaena crude extract and Fe3O4 with concentration of 370 mg eq BSA L-1 and 50 mg L-1 respectively, proportional to the adsorbed protein at the best magnetic coagulant dosage (420 mg L-1). It could be observed that significant removal was obtained at the first 20 min and became relatively constant until 60 min. This observation showed the significance of Fe3O4 in the magnetic coagulant that increased the removal kinetics, compared to leucaena crude extract that need 40 min before reached constant. It could be also observed in Fig. 5b, the Fe3O4 did not contribute to the Congo red removal, indicating the leucaena protein was the active coagulating agent.
The Congo red removal kinetics was further investigated using various kinetic models, namely: pseudo 1st order, pseudo 2nd order, Elovich, and interparticle diffusion models. It is known that coagulation mechanism in this study was charge neutralization which is usually preceded by adsorption of dye molecules on active coagulating agent. The adsorption step usually becomes the rate determining step in coagulation study, making adsorption models suitable for removal evaluation [47]. According to Obiora-Okafo et al. [48], this phenomenon is possible due to the polymeric nature of natural coagulants. The fitting result of various kinetic models is presented in Table 1, and sample of model plots is presented in Fig. 6. Based on the R2 value, it could be seen that pseudo 2nd order kinetics was highly suitable for kinetics modeling with R2 value of 0.99, while the Elovich and intra-particle diffusion models also gave good model-data correlation with R2 value around 0.70 to 0.90. Suitability of the pseudo 2nd order and Elovich kinetics to the removal of Congo red implied that the adsorption occurred during coagulation was chemisorption. It was possible due to the different charges between proteins on the magnetic coagulant and the Congo red molecules, making dipole-dipole interaction possible [49]. A 2-phase plot was observed in the interparticle diffusion model (Fig. 6d), indicating there are 2 determining step, namely surface adsorption followed by intra-particle diffusion. Similar conclusions of removal kinetic were also obtained in previous researches [6, 10, 50, 51].
Based on the characterization results and suitability of the kinetic models, an illustration of coagulation mechanism is presented in Fig. 7. One of –COOH of citrate ions was adsorbed to the surface of Fe3O4, while the others were available for protein binding. The overall magnetic coagulant was positively charged, following the charge of leucaena protein adsorbed on Fe3O4-CA, thus neutralizing the negatively charged Congo red molecules. The measurement of PV was done at the best magnetic coagulant condition (pH 3, dosage of 420 mg L-1). Initial Congo red wastewater had PV of 8.6 mg KMnO4 L-1, and water treated using leucaena crude extract showed 15.0 mg KMnO4 L-1 (increase of 49%). This increase was possible due to the presence of various soluble organic compounds in the crude extract. The magnetic coagulant showed lower increase of PV (18%), compared to the leucaena crude extract, due to desorbed protein in the treated wastewater.
This study focused on synthesis of magnetic coagulant by means of leucaena protein adsorption on the surface of citrate modified Fe3O4. Various trisodium citrate concentration and protein adsorption pH was investigated. Trisodium citrate was found to act as bridge between Fe3O4 and protein molecules, where at concentration of 0.5 M and pH 4.0, the highest protein adsorption was achieved. Further trisodium citrate concentration did not give any increase in protein adsorption. The functionalization of Fe3O4 did not change the morphology and crystallinity, however, bigger average crystal size was observed after protein functionalization. The adsorption of citrate and protein on the surface of Fe3O4 was confirmed by using FTIR analysis. The obtained magnetic coagulant was tested for its coagulation performance. At various coagulation pH, the highest removal was obtained at pH 3, indicating charge neutralization mechanism due to the positively charged protein at pH around 3. At various magnetic coagulant dosages, the increase of magnetic coagulant dosage increased the removal of Congo red, until the highest removal at 420 mg L-1. Further increase did not give any effect to the removal. From investigation using several kinetic models, it was found that the removal kinetic was well fitted with pseudo 2nd order kinetic model, reflected in high R2 value (> 0.99). The best coagulation was obtained at pH 3 and dosage of 420 mg L-1 with 80% removal. This result was comparable with crude extract of leucaena with half settling time (20 min) and lower increase of permanganate value. While this preliminary study shows that leucaena protein adsorbed on citrate modified Fe3O4 system may serve as a promising coagulant, further research is needed before this natural coagulant can be utilized for practical applications. Further systematic experiments to study the effect of several parameters affecting coagulation in real wastewater, such as conductivity of various background ions and wastewater temperature will be carried out, and the results will be reported in the forthcoming papers.
Availability of data and materials
All data generated or analyzed during this study are included in this article. The raw data are available from the corresponding author upon reasonable request.
Competing interests
The authors declare they have no competing interests.
Funding
This work was supported by Parahyangan Catholic University Centre of Research and Community Service with contract No III/LPPM/2020-01/09-P.
Authors' contributions
ER and HK carried out laboratory experimental studies and drafted the manuscript. HK, SP, and AKS designed the study and secured the funding. SP and AKS critically reviewed and edited the final manuscript. All the authors read and approved the final manuscript.
Acknowledgements
The authors acknowledged financial support by Parahyangan Catholic University Centre of Research and Community Service with contract No III/LPPM/2020-01/09-P. The authors also wish to thank all who have assisted in conducting this study.
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Table 1 Kinetics parameter of Congo red removal
|
Magnetic coagulant dosage (mg L-1) |
Pseudo 1st order |
Pseudo 2nd order |
Elovich |
Intra-particle diffusion |
|||||
|
k1 |
R2 |
k2 |
R2 |
α |
β |
R2 |
kd |
R2 |
|
|
60 |
0.044 |
0.491 |
0.027 |
0.994 |
246 |
0.192 |
0.826 |
7.0 |
0.9061 |
|
120 |
0.046 |
0.4004 |
0.035 |
0.9984 |
1541 |
0.313 |
0.7375 |
7.2 |
0.9369 |
|
180 |
0.041 |
0.4664 |
0.039 |
0.9983 |
944 |
0.345 |
0.7646 |
5.5 |
0.904 |
|
240 |
0.043 |
0.415 |
0.050 |
0.9974 |
2501 |
0.437 |
0.8708 |
5.4 |
0.9306 |
|
300 |
0.051 |
0.5889 |
0.055 |
0.9988 |
4237 |
0.528 |
0.7435 |
4.8 |
0.9156 |
|
360 |
0.031 |
0.0126 |
0.034 |
0.9984 |
123 |
0.349 |
0.9046 |
4.5 |
0.9412 |
|
420 |
0.049 |
0.4313 |
0.039 |
0.9979 |
149 |
0.402 |
0.7797 |
4.4 |
0.9652 |
|
480 |
0.033 |
0.2475 |
0.044 |
0.998 |
70 |
0.401 |
0.8236 |
3.9 |
0.9694 |
|
540 |
0.029 |
0.2036 |
0.043 |
0.9977 |
47 |
0.438 |
0.8785 |
3.3 |
0.9692 |
|
600 |
0.036 |
0.3235 |
0.057 |
0.9983 |
82 |
0.529 |
0.82 |
3.1 |
0.9658 |
|
370a |
0.055 |
0.4313 |
0.039 |
0.9978 |
7 |
0.175 |
0.9674 |
3.8 |
0.9818 |
|
50b |
0.021 |
0.6233 |
0.049 |
0.5314 |
0.2 |
0.229 |
0.9325 |
0.78 |
0.7808 |
aLeucaena crude extract (mg eq BSA L-1), bFe3O4 (mg L-1)