Research Article | | Peer-Reviewed

Enhanced Solubility of Herbicide Diuron in Aqueous Solution by Micellisation

Received: 17 October 2025     Accepted: 6 November 2025     Published: 17 December 2025
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Abstract

Surfactants are substances widely used in agricultural sprays to improve the solubility and mobility of pesticides across crops. This study investigates the micellar properties of two ionic surfactants sodium dodecyl sulfate (SDS) and tetramethylammonium tetrafluoroborate (TMATFB) with respect to their ability to solubilize the herbicide diuron in aqueous solution. Conductometric measurements were performed in aqueous media over a temperature range of 298 to 331 K to analyze the micellization behavior and evaluate the efficiency of solubilization. From the conductivity data the critical micelle concentration (CMC), and degree of ionization were obtained at various temperatures. Concentration and temperature effect on the CMC have been studied and the different thermodynamic parameters were evaluated. The critical micellar concentration (CMC) values of surfactants decreased with increasing temperature, indicating enhanced micelle formation under thermal influence. Additionally, the solubility of diuron varied significantly across different surfactant micelles concentration, suggesting that specific interactions occur between the surfactant head groups and the pesticide. The standard Gibbs free energy (∆G°) for the diuron–surfactant mixtures was attained to be negative throughout the study suggesting spontaneous micellization process. The enthalpy (∆H°) and entropy (∆S°) were also evaluated, offering additional insight into the thermodynamic driving forces involved. The obtained thermodynamic parameters showed that |TΔS°| is greater than |ΔH°|, suggesting that the micellization process is controlled by entropy.

Published in American Journal of Physical Chemistry (Volume 14, Issue 4)
DOI 10.11648/j.ajpc.20251404.12
Page(s) 100-109
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2025. Published by Science Publishing Group

Keywords

Diuron, Herbicide, Surfactants, Solubilisation, Water

1. Introduction
Pesticides are substances applied to crops to control pests. Their use is of considerable importance in agriculture, as they contribute to increased crop yields. Furthermore, pesticides have helped reduce production disruptions caused by severe pest infestations and have played a key role in combating hunger by protecting both crops in the field and stored food reserves . However, the large-scale use of pesticides can lead to indirect and harmful effects on the environment. Numerous studies have reported the presence of pesticide residues in food, as well as in surface and groundwater sources . During application, a significant portion of the pesticides does not reach the target crops and may persist in the environment for many years . Depending on the method of application and prevailing weather conditions, it is estimated that between 25% and 75% of pesticides fail to deposit on the intended treatment areas . Pesticides can enter the atmosphere directly during application, contaminating both the air and precipitation. Numerous studies have shown that this form of pollution is not limited to agricultural areas, as atmospheric conditions such as wind, temperature, and pressure differences can facilitate the transport of pesticide particles to urban environments . This atmospheric diffusion can occur over long distances and affect regions far from the original site of application.
This study focuses on the herbicide diuron. Herbicides are a class of pesticides used to eliminate weeds that hinder the healthy growth of crops, and their use is widespread in modern agriculture. Among the various types of herbicides, some offer total weed control, removing all vegetation exposed to the chemical, while others provide selective weed control, targeting specific weed species without significantly harming the cultivated crops . Herbicide degradation occurs when the compound is broken down into smaller molecules ultimately into carbon dioxide and water through photochemical, chemical, or biological processes . Degradation can also occur through adsorption by plants or soil, as well as through leaching into deeper soil layers via drainage . When an herbicide is degraded in the environment, it produces several by-products known as metabolites. Each metabolite has its own chemical properties, including specific levels of toxicity, adsorption capacity, and resistance to further degradation. In many cases, the exact nature and behavior of these metabolites remain largely unknown . Some may contain substances capable of harming terrestrial ecosystems .
In Senegal, most sprayed anti-parasitic compounds are widely used in a major agricultural region known as the Niayes Area, where farming is practiced year-round . Diuron, like many other herbicides, is extensively applied in this region to increase crop yields by eliminating weeds. Many of these compounds exhibit significant photochemical instability, especially under the Niayes Area’s sunny, warm, and dry summer climate, which accelerates their degradation in the environment . To address concerns related to pollution and toxicity, numerous analytical methods for detecting diuron have been reported in the literature. These methods primarily rely on chromatography, combined with spectroscopic or electrochemical techniques . The direct fluorescence (DF), photochemically induced fluorescence (PIF) and UV-visible methods .
However, these accurate and reliable methods are often time-consuming and require the use of expensive instruments and skilled handling. In contrast, conductometric methods offer several advantages, including lower equipment costs, simpler sample preparation, faster analysis, high sensitivity, and good overall performance. Micellar solubilisation is an effective approach to enhance the solubility of organic substances that are poorly soluble in water. For this reason, we have undertaken a study of the interaction between the herbicide diuron and surfactants in aqueous solution using conductometric methods.
2. Materials and Methods
2.1. Apparatus
A VWR CO 3100L Conductometer, equipped with a measuring cell of constant 0.84 cm-1 and a temperature probe, was used for the conductometric measurements. The apparatus was calibrated using a 0.01 M KCl solution with conductivities of 1278 and 1413 µS/cm at 20°C and 25°C, respectively. A VELP SCIENTIFICA heating magnetic stirrer was employed for sample mixing. Weighing was performed using a Sartorius U3600S electronic balance with a precision of 0.1 mg.
2.2. Reagents
Diuron (98% w/w) was purchased from Sigma-Aldrich Chemical Company (USA) and was used without purification. Sodium dodecyl sulfate (SDS 98%, m/m) and tetramethyl ammonium tetrafluoroborate (TMATFB [(CH3)4 N+, BF4-] 97% m/m) were purchased from Sigma Aldrich. Distilled water is used to prepare surfactant stock solutions. The chemical properties of diuron and surfactants are presented in Table 1.
Table 1. Chemical properties of diuron and surfactants .

Product

Formula

Molar mass (g mol−1)

WS (25 °C) (mg L−1)

MP (°C)

BP (°C)

Structure

Diuron

C9H10Cl2N2O

233.095

45

158

180

SDS

CH3(CH2)11SO4Na

288.38

1000

206

NF

TMATFB

(CH3)4NBF4

160.95

NF

NF

NF

WS = Water solubility; MP = Melting point; BP = Boiling point.
2.3. Solutions Preparation
Stock solutions of diuron (10-3 mol·L-1) were freshly prepared in methanol and surfactants (SDS and TMATFB) in distilled water at 0.5 mol·L-1. These solutions were subsequently diluted to obtain the desired working concentrations. All solutions were stored in glass vials wrapped with aluminum foil and kept in a refrigerator, protected from light and heat to prevent decomposition.
2.4. Conductivity Measurements
Conductivities were performed with a digital conductivity meter (A VWR CO 3100 LK) well-appointed with a measuring cell and a temperature sensor. The dosing temperature is set to a specific value, and volumes of 0.2 mL of the titrant solution are taken and then poured each time into a beaker containing 150 mL of a pesticide solution of known concentration using a graduated burette and filled with the surfactant solution. The beaker is placed on a heating magnetic stirrer and the mixture was homogenized magnetically during 10 seconds before we noted the specific conductivity.
2.5. Determination Method of Thermodynamic Parameters of Micelles
The surfactants studied being ionic, of monovalent types (a single hydrophobic chain), the standard free enthalpy of micellisation can be determined by the relationship below: .
G°=2-αRTlnX CMC(1)
Where α is the degree of dissociation, R is gas constant and T is the temperature in Kelvin scale. XCMC is the mole fraction at CMC of the ionic liquids.
H°= -T2ddTG°T (2)
By replacing equation (1) in equation (2), and if we consider a short temperature interval, we obtain:
H°=-RT2(2-α)ddT(lnX CMC)(3)
The values of lnXcmc vary linear way as a function of temperature which can be presented by following Eq. (3). The term d dT (lnXCMC) corresponds to the slope of the line lnXCMC = f(T).
The entropy associated with the micellisation process can be calculated using the following: equation:
S°=1T  (H°-G°)(4)
3. Results and Discussion
3.1. Effect of Diuron on the CMC and α
We followed the evolution of the specific conductivity of a solution containing a fixed and known concentration of diuron as a function of the concentration of ionic surfactants (SDS and TMATFB). Figure 1 present plots of the specific conductivity according to the TMATFB and SDS concentration in water in the absence and the presence of diuron at 298 K. We observe a variation in the specific conductivity as a function of the concentrations of the surfactants. The CMC values were determined by measuring the change in specific conductivity values with the addition of surfactants. This also vary depending on the diuron concentration . Two specific conductivity-dependent regimes were observed below and above the CMC. The corresponding value to the breaking point was taken as the CMC for the system . The increase in specific conductivity can be explained by the increase in the number of free counterions (BF4- or Na+) in the solution . Degree of ionization of micelles, α can be obtained from the ratio of the slopes above and below the CMC. The values of CMC and α obtained from the specific conductivity plots are listed in Table 2 at different concentration of diuron. Micellar solubilization depends on the type of surfactant, the solute (diuron), and the interactions between the solvent and solute . To better understand the specific influence of surfactants on the conductivity of diuron, we studied the conductivity as a function of diuron concentration in the absence of surfactants.
Figure 1. Variation of specific conductivity with TMATFB and SDS concentrations in the absence and presence of diuron at 298 K.
As observed, the specific conductivity of diuron changes only slightly in the absence of surfactants, indicating that surfactants significantly influence conductivity. The pronounced variations in specific conductivity shown in Figure 2 are therefore attributed to the presence of the ionic surfactants TMATFB and SDS. Pesticide solubility in the micelles are cooperatively affected by pesticide hydrophobicity, surfactant head type and micellar structure . The estimated CMC, α, and ΔG⁰ α values of the diuron+surfactants system in aqueous medium are presented in Table 2.
For both surfactants, a decrease in the critical micelle concentration (CMC) was observed with increasing diuron concentration (Figure 2). This decrease was more pronounced for the cationic surfactant (TMATFB). To better understand this trend, it is useful to examine the chemical structure of diuron, which may help explain the reduction in CMC as diuron concentration increases. Due to its molecular structure, Diuron possesses a high dipole moment, enabling strong interactions with the polar head groups of surfactants such as SDS and TMATFB in solution . This interaction facilitates the formation of aggregates with highly hydrophobic organic compounds, promoting micellar solubilisation . Diuron enhances the activity of both TMATFB and SDS by adsorbing at the interface, simultaneously reducing the surface tension of the micelles .
Figure 2. Variation of CMC for TMATFB (A) and SDS (B) as a function of diuron concentration at 298 K.
Table 2. CMC, α and ΔG0 values as a function of diuron concentration at 298 K.

[Diur] (mM)

SDS

TMATFB

CMCa (mM)

αb (%)

ΔG° c (kJ mol-1)

CMCa (mM)

α b (%)

ΔG° c (kJ mol-1)

0

13.62

0.340

-21.86

15.97

0.359

-20.93

5

13.14

0.290

-22.65

15.03

0.368

-21.44

10

12.67

0.249

-22.65

15.03

0.368

-21.44

15

12.19

0.247

-23.52

13.14

0.471

-20.47

20

11.72

0.232

-23.91

12.19

0.503

-20.94

a Critical micellar concentration; b Degree of dissociation; c Gibbs free enthalpy; mM = 10-3 mol L-1
However, opposite trends in the variation of the degree of micellar ionization (α) with increasing diuron concentration are observed for SDS and TMATFB (Figure 3). The mechanism of micellar solubilisation of Diuron differs between SDS and TMATFB. In the presence of TMATFB, the increase in α values reflects micellar interactions involving the polar head groups of the surfactants and diuron . Conversely, in SDS, α decreases with increasing diuron concentration, indicating a strengthening of hydrophobic interactions. These results demonstrate that diuron solubilizes within the micelle core . In conclusion, diuron exhibits greater solubilisation in SDS compared to TMATFB. The standard Gibbs free energy change (ΔG°) generally increases with Diuron concentration. In aqueous solution, the presence of diuron significantly promotes micelle formation, thereby reducing the critical micelle concentration (CMC). Diuron effectively acts as a co-surfactant during the micellisation process of both SDS and TMATFB.
Figure 3. Variation of α for TMATFB (A) and SDS (B) as a function of diuron concentration at 298 K.
3.2. Determination of the Krafft Temperature
The Krafft temperature is the minimum temperature at which micellar aggregates are formed. Using surfactant concentrations above the CMC (15.50 mM for SDS and 19.23 mM for TMATFB), we investigated the variation of diuron specific conductivity as a function of temperature (Figure 4). The resulting curves exhibited three distinct regions, from which the Krafft temperature was determined based on changes in slope. The Krafft temperatures were found to be 11 °C for SDS and 22 °C for TMATFB, with an uncertainty of ±1 °C.
Figure 4. Variation of the specific conductivity of surfactants SDS and TMATFB as a function of temperature.
3.3. Temperature Effect on the CMC and α
Figure 5 shows the variation of specific conductivity as a function of surfactant concentration at 298 K, 303 K, 310 K, 317 K, 324 K, and 331 K, in the presence of 15.10-6 M diuron. For both surfactants studied, temperature has a significant effect on the solubilisation of diuron in water . The CMC decreases with increasing temperature, enhancing adsorption at the interface and simultaneously reducing the surface tension of the micelles . The increase in temperature can also disrupt the structured water molecules surrounding the hydrophobic groups (linear chains of the surfactants), this could lead to increased dehydration of the hydrophilic heads, favoring to faster micellisation . In the presence of SDS, the micellar solubilisation of diuron results in co-micellisation, forming mixed micelles containing both SDS and diuron. The decrease in the dissociation coefficient with rising temperature likely reflects stronger hydrophobic interactions. The increase in α with TMATFB indicates that diuron resides between the surfactant’s polar head groups during solubilisation. To verify the actual influence of surfactants on the specific conductivity of diuron at different temperatures, we studied the conductivity in the presence of diuron (15.10-6 M) without surfactants (Figure 6). No variation in specific conductivity was observed. This shows that temperature has no effect on the variation in the conductivity of the diuron molecule.
Figure 5. Specific conductivity of SDS (A) and TMATFB (B) in the presence of 15×10-6 M diuron as a function of surfactant concentration at temperatures of 298, 303, 310, 317, 324, and 331 K.
Figure 6. Variation of specific conductivity of diuron (15×10-6 M) without surfactants at different temperatures: 298 K, 303 K, 310 K, 317 K, 324 K, and 331 K.
3.4. Thermodynamic Parameters
The thermodynamic parameters ΔG⁰, ΔH⁰, and ΔS⁰ were calculated with the help equations (1), (2) et (3). The slope d(lnXCMC)/dT was derived from the plot of lnXCMC versus temperature (Figure 7). As shown, lnXCMC decreases with increasing temperature. Furthermore, the negative values of ΔG⁰ confirm that the micellisation process is spontaneous and thermodynamically favorable (Table 3). The Gibbs free energy decreases as the temperature increases; consequently, the micellisation of diuron will be favored at higher temperatures. The values of ΔH⁰ > 0 indicate an endothermic process. |TΔS°| > |ΔH°| shows that the association of diuron with TMATFB and SDS is entropy-driven, with the enthalpy increase during micellisation compensated by the system’s increased disorder. This increase in entropy arises from the aggregation of hydrophobic chains and the release of counter-ions. It can also be stated that the micellization of surfactants with diuron is governed by the aggregation of the latter. Moreover, it is well established that micellisation is driven by the entropic contribution .
Figure 7. Representation of lnXCMC of surfactants (SDS, TMATFB) as a function of temperature.
Table 3. Micellisation and thermodynamic parameters values of diuron at different temperatures.

Surfactants

T (K)

cmcx103 M

XCMC

α (%)

G° (KJ moL-1)

H° (KJ moL-1)

TS° (KJ moL-1)

SDS

303

8.36

0.91 10-4

0.759

-27.88

17.98

41.22

310

7.34

0.84 10-4

0.725

-29.52

19.32

42.86

317

6.42

0.80 10-4

0.533

-35.31

23.25

50.50

324

5.44

0.74 10-4

0.358

-41.20

27.18

57.60

331

4.46

0.71 10-4

0.323

-43.50

28.98

59.78

TMATFB

303

12.69

2.29 10-4

0.260

-23.149

5.25

38.49

310

12.19

2.41 10-4

0.318

-23.512

5.53

39.31

317

11.24

2.09 10-4

0.303

-24.627

5.80

39.58

324

10.30

2.07 10-4

0.336

-25.082

6.27

41.22

331

8.36

2.02 10-4

0.395

-25.623

6.56

41.49

4. Conclusion
In this study, the interaction of diuron with surfactants such as SDS and TMATFB was investigated using conductometric measurements at different temperatures. The presence of diuron in aqueous surfactant solutions led to a decrease in the critical micellar concentration (CMC), with this effect becoming more pronounced at higher pesticide concentrations and temperatures. Furthermore, the Gibbs free energy (∆G°) values of the diuron–surfactant system in aqueous solution were all negative, indicating that micellar aggregation is spontaneous. The positive enthalpy (∆H°) values suggest that micellisation is an endothermic process. Additionally, the positive entropy (∆S°) values observed at higher temperatures imply that micellisation of the diuron-surfactant mixture is predominantly driven by entropy. The results clearly demonstrate that micellar solubilization is an effective means for enhancing the solubility of poorly water-soluble pesticides. This work is a key element of our strategy to reduce the presence and persistence of these pesticides in natural waters.
Abbreviations

CMC

Critical Micellar Concentration

Acknowledgments
One of us, S. Sambou warmly thanks the Service of Cooperation and Cultural Action (SAC) of the French Embassy in Dakar (Senegal) for financial support of his research stay in the University of the Littoral Côte d’Opale (Dunkerque, France) and the University of the Bretagne Occidentale (Brest, France).
Author Contributions
Souleymane Sambou: Writing – original draft, Investigation, Conceptualization
Ibrahima Sarr: Data curation, Resources
Nehou Diouf: Formal Analysis
Coumba Faye: Visualization, Data curation
Abdou Khadre Cisse: Methodology, Formal Analysis
Boubacar Sidibe: Visualization
Aly Cisse: Data curation
Keba Diongue: Data curation, Methodology
El Hadji Tombe Bodian: Writing – original draft, Methodology, Supervision, Validation
Diene Diegane Thiare: Writing – original draft, Validation, Supervision, Conceptualization.
Atanasse Coly: Validation, Supervision
Funding
This work is supported by the Service of Cooperation and Cultural Action (SAC) of the French Embassy in Dakar (Senegal), (Grant numbers 968932 K).
Data Availability Statement
No data was used.
Conflicts of Interest
The authors declare no conflicts of interest.
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Cite This Article
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    Sambou, S., Sarr, I., Diouf, N., Faye, C., Cisse, A. K., et al. (2025). Enhanced Solubility of Herbicide Diuron in Aqueous Solution by Micellisation. American Journal of Physical Chemistry, 14(4), 100-109. https://doi.org/10.11648/j.ajpc.20251404.12

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    Sambou, S.; Sarr, I.; Diouf, N.; Faye, C.; Cisse, A. K., et al. Enhanced Solubility of Herbicide Diuron in Aqueous Solution by Micellisation. Am. J. Phys. Chem. 2025, 14(4), 100-109. doi: 10.11648/j.ajpc.20251404.12

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    AMA Style

    Sambou S, Sarr I, Diouf N, Faye C, Cisse AK, et al. Enhanced Solubility of Herbicide Diuron in Aqueous Solution by Micellisation. Am J Phys Chem. 2025;14(4):100-109. doi: 10.11648/j.ajpc.20251404.12

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  • @article{10.11648/j.ajpc.20251404.12,
      author = {Souleymane Sambou and Ibrahima Sarr and Nehou Diouf and Coumba Faye and Abdou Khadre Cisse and Boubacar Sidibe and Aly Cisse and Keba Diongue and El Hadji Tombe Bodian and Diene Diegane Thiare and Atanasse Coly},
      title = {Enhanced Solubility of Herbicide Diuron in Aqueous Solution by Micellisation},
      journal = {American Journal of Physical Chemistry},
      volume = {14},
      number = {4},
      pages = {100-109},
      doi = {10.11648/j.ajpc.20251404.12},
      url = {https://doi.org/10.11648/j.ajpc.20251404.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ajpc.20251404.12},
      abstract = {Surfactants are substances widely used in agricultural sprays to improve the solubility and mobility of pesticides across crops. This study investigates the micellar properties of two ionic surfactants sodium dodecyl sulfate (SDS) and tetramethylammonium tetrafluoroborate (TMATFB) with respect to their ability to solubilize the herbicide diuron in aqueous solution. Conductometric measurements were performed in aqueous media over a temperature range of 298 to 331 K to analyze the micellization behavior and evaluate the efficiency of solubilization. From the conductivity data the critical micelle concentration (CMC), and degree of ionization were obtained at various temperatures. Concentration and temperature effect on the CMC have been studied and the different thermodynamic parameters were evaluated. The critical micellar concentration (CMC) values of surfactants decreased with increasing temperature, indicating enhanced micelle formation under thermal influence. Additionally, the solubility of diuron varied significantly across different surfactant micelles concentration, suggesting that specific interactions occur between the surfactant head groups and the pesticide. The standard Gibbs free energy (∆G°) for the diuron–surfactant mixtures was attained to be negative throughout the study suggesting spontaneous micellization process. The enthalpy (∆H°) and entropy (∆S°) were also evaluated, offering additional insight into the thermodynamic driving forces involved. The obtained thermodynamic parameters showed that |TΔS°| is greater than |ΔH°|, suggesting that the micellization process is controlled by entropy.},
     year = {2025}
    }
    

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  • TY  - JOUR
    T1  - Enhanced Solubility of Herbicide Diuron in Aqueous Solution by Micellisation
    AU  - Souleymane Sambou
    AU  - Ibrahima Sarr
    AU  - Nehou Diouf
    AU  - Coumba Faye
    AU  - Abdou Khadre Cisse
    AU  - Boubacar Sidibe
    AU  - Aly Cisse
    AU  - Keba Diongue
    AU  - El Hadji Tombe Bodian
    AU  - Diene Diegane Thiare
    AU  - Atanasse Coly
    Y1  - 2025/12/17
    PY  - 2025
    N1  - https://doi.org/10.11648/j.ajpc.20251404.12
    DO  - 10.11648/j.ajpc.20251404.12
    T2  - American Journal of Physical Chemistry
    JF  - American Journal of Physical Chemistry
    JO  - American Journal of Physical Chemistry
    SP  - 100
    EP  - 109
    PB  - Science Publishing Group
    SN  - 2327-2449
    UR  - https://doi.org/10.11648/j.ajpc.20251404.12
    AB  - Surfactants are substances widely used in agricultural sprays to improve the solubility and mobility of pesticides across crops. This study investigates the micellar properties of two ionic surfactants sodium dodecyl sulfate (SDS) and tetramethylammonium tetrafluoroborate (TMATFB) with respect to their ability to solubilize the herbicide diuron in aqueous solution. Conductometric measurements were performed in aqueous media over a temperature range of 298 to 331 K to analyze the micellization behavior and evaluate the efficiency of solubilization. From the conductivity data the critical micelle concentration (CMC), and degree of ionization were obtained at various temperatures. Concentration and temperature effect on the CMC have been studied and the different thermodynamic parameters were evaluated. The critical micellar concentration (CMC) values of surfactants decreased with increasing temperature, indicating enhanced micelle formation under thermal influence. Additionally, the solubility of diuron varied significantly across different surfactant micelles concentration, suggesting that specific interactions occur between the surfactant head groups and the pesticide. The standard Gibbs free energy (∆G°) for the diuron–surfactant mixtures was attained to be negative throughout the study suggesting spontaneous micellization process. The enthalpy (∆H°) and entropy (∆S°) were also evaluated, offering additional insight into the thermodynamic driving forces involved. The obtained thermodynamic parameters showed that |TΔS°| is greater than |ΔH°|, suggesting that the micellization process is controlled by entropy.
    VL  - 14
    IS  - 4
    ER  - 

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