Hydrotrope

A hydrotrope is a compound that solubilises hydrophobic compounds in aqueous solutions. Typically, hydrotropes consist of a hydrophilic part and a hydrophobic part (like surfactants) but the hydrophobic part is generally too small to cause spontaneous self-aggregation.
Hydrotropes do not have a critical concentration above which self-aggregation 'suddenly' starts to occur (as found for micelle- and vesicle-forming surfactants, which have a critical micelle concentration or cmc and a critical vesicle concentration or cvc, respectively). Instead, some hydrotropes aggregate in a step-wise self-aggregation process, gradually increasing aggregation size. However, many hydrotropes do not seem to self-aggregate at all, unless a solubilisate has been added. Hydrotropes are in use industrially. Examples of hydrotropes include sodium p-toluenesulfonate and sodium xylene sulfonate.

The term hydrotropy was originally put forward by Carl Neuberg[1] to describe the increase in the solubility of a solute by the addition of fairly high concentrations of alkali metal salts of various organic acids. However, the term has been used in the literature to designate non-micelle-forming substances, either liquids or solids, organic or inorganic, capable of solubilizing insoluble compounds.

The chemical structure of the conventional Neuberg’s hydrotropic salts (proto-type, sodium benzoate) consists generally of two essential parts, an anionic group and a hydrophobic aromatic ring or ring system. The anionic group is involved in bringing about high aqueous solubility, which is a prerequisite for a hydrotropic substance. The type of anion or metal ion appeared to have a minor effect on the phenomenon.[1] On the other hand, planarity of the hydrophobic part has been emphasized as an important factor in the mechanism of hydrotropic solubilization[2][3]

To form a hydrotrope, an aromatic hydrocarbon solvent is sulfonated creating an aromatic sulfonic acid. It is then neutralized with a base.[4]

Additives may either increase or decrease the solubility of a solute in a given solvent. These salts that increase solubility are said to ‘salt in’ the solute and those salts that decrease the solubility ‘salt out’ the solute. The effect of an additive depends very much on the influence, it has on the structure of water or its ability to compete with the solvent water molecules.[5] A convenient quantitation of the effect of a solute additive on the solubility of another solute may be obtained by the Setschetow equation:[6]

\log{\frac {S_0}{S}} = K \cdot C_a; where
S0 = solubility in the absence of the additive
S = solubility in the presence of the additive
Ca = concentration of the additive
K = salting coefficient, which is a measure of the sensitivity of the activity coefficient of the solute towards the salt.

Applications

Hydrotropes are in use industrially and commercially in cleaning and personal care product formulations to allow more concentrated formulations of surfactants. About 29,000 metric tons are produced (i.e., manufactured and imported) annually in the US.[4] Annual production (plus importation) in Europe and Australia is approximately 17,000 and 1,100 metric tons, respectively.[7][8] Common products containing a hydrotropes include laundry detergents, surface cleaners, dishwashing detergents, liquid soaps, shampoos and conditioners.[4] They are coupling agents, used at concentrations from 0.1-15% to stabilize the formula, modify viscosity and cloud-point, reduce phase separation in low temperatures, and limit foaming.[8]

Examples of Hydrotropes used for industrial and commercial purposes [4][7]

Chemical CAS#
Toluene sulfonic acid, Na salt 12068-03-0
Toluene sulfonic acid, K salt 16106-44-8

30526-22-8

Xylene sulfonic acid, Na salt 1300-72-7

827-21-4

Xylene sulfonic acid, ammonium salt 26447-10-9
Xylene sulfonic acid, K salt 30346-73-7
Xylene sulfonic acid, Ca salt 28088-63-3
Cumene sulfonic acid, Na salt 28348-53-0

32073-22-6

Cumene sulfonic acid, ammonium salt 37475-88-0

Environmental Considerations

Hydrotropes have a low bioaccumulation potential, as the octanol:water partition coefficient is <1.0.[4] Studies have found hydrotopes to be very slightly volatile, with vapour pressures <2.0x10-5 Pa.[4] They are aerobically biodegradable. Removal via the secondary wastewater treatment process of activated sludge is >94%.[8] Acute toxicity studies on fish show an LC50 >400 mg active ingredient (a.i.)/L. For Daphnia, the EC50 is >318 mg a.i./L. The most sensitive species is green algae with EC50 values in the range of 230–236 mg a.i./ L and No Observed Effect Concentrations (NOEC) in the range of 31–75 mg a.i./L.[8] The aquatic Predicted No Effect Concentration (PNEC) was found to be 0.23 mg a.i./L.[7] The Predicted Environmental Concentration (PEC)/PNEC ratio has been determined to be < 1 and, therefore, hydrotropes in household laundry and cleaning products have been determined to not be an environmental concern.[4][7]

Human Health

Aggregate exposures to consumers (direct and indirect dermal contact, ingestion, and inhalation) have been estimated to be 1.42 ug/Kg bw/day.[7] Animal studies do not suggest sensitization, but there are no reliable human data available.[8] Calcium xylene sulfonate and sodium cumene sulfonate have been shown to cause temporary, slight eye irritation in animals.[8] Studies have not found hydrotropes to be mutagenic, carcinogenic or have reproductive toxicity.[8]

References

  1. ↑ 1.0 1.1 Neuberg, C., Biochem. Z., 1916, 76, 107.
  2. ↑ Evstigneev, M.P., Evstigneev V.P., Hernandez Santiago A.A., Davies, David B. 2006. Effect of a mixture of caffeine and nicotinamide on the solubility of vitamin (B2) in aqueous solution. European Journal of Pharmaceutical Sciences 28 (1-2) 59-66.
  3. ↑ Suzuki,H., Sunada, H., 1998. Mechanistic studies on hydrotropic solubilization of nifedipine in nicotinamide solution, Chem & Pharm Bulletin.46 (1) 125-130.
  4. ↑ 4.0 4.1 4.2 4.3 4.4 4.5 4.6 Stanton, Kathleen; Caritas Tibazarwa; Hans Certa; William Greggs; Donna Hillebold; Lela Jovanovich; Daniel Woltering; Richard Sedlak (2010). "Environmental Risk Assessment of Hydrotropes in the United States, Europe, and Australia.". Integrated Environmental Assessment and Management 6 (1): 155–163. doi:10.1897/IEAM_2009-019.1.
  5. ↑ Da Silva, R.C., Spitzer, M., Da Silva, L.H.M., Loh, W., 1999. Investigations on the mechanism of aqueous solubility increase caused by some hydrotropes, Thermochimica Acta., 328, 161-167.
  6. ↑ Singhai, A., 1992. Studies on solubilization, formulation and evaluation of some drugs, Dept. of Pharm. Sci. Dr. H. S. Gaur vishwavidhyalaya., Sagar, 10.
  7. ↑ 7.0 7.1 7.2 7.3 7.4 Human & Environmental Risk Assessment on ingredients of household cleaning products (HERA) (2005). "Hydrotropes". Risk Assessment.
  8. ↑ 8.0 8.1 8.2 8.3 8.4 8.5 8.6 Hydrotropes Consortium (2005). "SIDS Initial Assessment Report for SIAM 21 Hydrotropes.".