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ORIGINAL ARTICLE
Creation of Novel Green and Sustainable Gemini-Type CationicsContaining Carbonate Linkages
Taisuke Banno • Kazuo Kawada • Shuichi Matsumura
Received: 23 March 2010 / Accepted: 8 July 2010 / Published online: 5 August 2010
� AOCS 2010
Abstract Novel gemini-type cationics containing
carbonate linkages as biodegradable and chemically recy-
clable segments were designed and synthesized by a green
process. The carbonate linkages were introduced into only
the hydrophobic moiety or in both the hydrophobic and
linker moieties of gemini-type cationics. They showed
higher surface activities, such as a low critical micelle
concentration value, a surface tension lowering, and a high
adsorption efficiency, when compared to the corresponding
single-type cationics. Also, the gemini-type cationics con-
taining carbonate linkages in both the hydrophobic and the
linker moieties showed stronger antimicrobial activities
when compared to those only in the hydrophobic moiety. It
was found that some gemini-type cationics containing
carbonate linkages showed higher biodegradability com-
pared to the conventional gemini-type cationics. The bio-
degradability of the gemini-type cationics decreased when
a carbonate linkage was introduced into the hydrophobic
moiety rather than the linker moiety. However, some
gemini-type cationics containing carbonate linkages both
in the hydrophobic and linker moieties showed ready bio-
degradability. The gemini-type cationics containing car-
bonate linkages in the hydrophobic moiety showed
chemical recyclability by a lipase (E.C. 3.1.1.3).
Keywords Antimicrobial activity � Biodegradability �Carbonate linkage � Chemical recyclability � Gemini-type
cationic surfactant � Green chemistry � Lipase � Surface
activity
Introduction
In recent years, the establishment of the new field of
green chemistry has been recognized as a necessary goal
for sustainable development. This greening of chemistry
has realized the discovery and development of new
synthetic routes using renewable feedstocks, reaction
conditions and catalysts for improved selectivity and
energy minimization, and the design of bio-/environ-
mentally compatible chemicals. Based on these concepts,
some green surfactants have been designed and synthe-
sized using bio-based or potentially bio-based starting
materials, such as amino acids, fumaric acid, maleic
acid, and aconitic acid [1–3].
The syntheses and properties of gemini-type (dimeric)
cationics consisting of two hydrophobic alkyl chains and
two quaternary ammonium groups covalently attached
through a linker moiety have been extensively studied by
many researchers. The first report of dimeric cationics in
the scientific literature was published by Bunton et al. [4].
The term ‘‘gemini-surfactants’’ was coined for these
dimeric surfactants by Menger et al. [5, 6]. It has been
reported that gemini-type cationics exhibited superior
properties when compared to those of conventional single-
type cationics, such as lower critical micelle concentration
(CMC), surface tension lowering, higher adsorption effi-
ciency, and so on [7–11]. Carbohydrate-based gemini-type
surfactants with two tertiary amino groups have been
synthesized and characterized [12–14]. Also, gemini-type
T. Banno � S. Matsumura (&)
Department of Applied Chemistry, Faculty of Science
and Technology, Keio University, 3-14-1, Hiyoshi,
Kohoku-ku, Yokohama 223-8522, Japan
e-mail: [email protected]
K. Kawada
Department of Chemistry, School of Science,
Kitasato University, 1-15-1, Kitasato,
Sagamihara 228-8555, Japan
123
J Surfact Deterg (2010) 13:387–398
DOI 10.1007/s11743-010-1224-5
cationics showed strong antimicrobial activities against a
broad range of microorganisms [15–17]. Gemini-type cat-
ionics can be regarded as green surfactants because they
show higher functionalities that lead to a reduction in their
consumption. This saves carbon resources and production
energies. However, there are few reports on the biode-
gradabilities of gemini-type cationics. Furthermore, cat-
ionics are generally resistant to biodegradation due to the
lack of a primary degradation site in the molecule [18].
Due to the water-soluble nature of surfactants, they are
generally difficult to recover or reuse. Once they are
discharged as drainage into the environment, they
are widely diffused if they are not biodegradable. Thus, the
development of gemini-type cationics with an improved
biodegradability using renewable resources by an envi-
ronmentally benign process is needed with respect to the
establishment of green and sustainable chemistry. It has
been reported that gemini-type cationics containing ester
linkages in the hydrophobic moiety were biodegraded by
activated sludge [19–21]. However, ester linkages are
generally labile to hydrolysis, particularly under alkaline
conditions. More hydrolytically stable and biodegradable
cationics are, thus, needed. Furthermore, gemini-type cat-
ionics should be chemically recyclable, particularly in the
industrial field.
The carbonate linkage is hydrolyzed by lipase in aque-
ous media to produce two hydroxyl groups with the evo-
lution of carbon dioxide. However, it is advantageous for
surfactants that, in the absence of lipase, carbonate linkages
are more stable than ester linkages in aqueous media
because they are generally used in aqueous solution.
A nonionic surfactant containing a carbonate linkage was
first reported by Stjerndahl and Holmberg [22]. The syn-
thetic polyoxyethylene-type nonionic surfactants contain-
ing carbonate linkages showed both hydrolytic stability and
biodegradability. We previously reported that single-type
cationic surfactants containing a carbonate linkage showed
antimicrobial activities, chemical recyclability, and biode-
gradability, in addition to good surfactant properties [23].
We also reported that biodegradability was improved by
the introduction of the carbonate linkage into the linker
moiety of gemini-type cationics [24].
In this report, novel gemini-type cationic green surfac-
tants containing carbonate linkages were designed and
synthesized by a green process. Figure 1 shows the design
of gemini-type cationics containing carbonate linkages as
biodegradable and chemically recyclable segments. The
carbonate linkages were introduced into only the hydro-
phobic moiety or in both the hydrophobic and linker
moieties of gemini-type cationics. Their surfactant prop-
erties, biodegradabilities, chemical recyclabilities, and
antimicrobial activities were evaluated.
Experimental Procedures
Materials and Methods
Diphenyl carbonate, 1-alkanols, 3-N,N-dimethylamino-
1-propanol, 1-N,N-dimethylamino-2-propanol, and methyl
iodide were purchased from Tokyo Kasei Kogyo Co., Ltd.
(Tokyo, Japan) and used as received. Triethylamine (Et3N)
was purchased from Sigma-Aldrich Co., Inc. (St. Louis,
MO, USA). 1,3-Diiodopropane was purchased from Wako
Chemical Co., Ltd. (Osaka, Japan) and used as received.
Immobilized lipase (E.C. 3.1.1.3) from Candida antarctica
[lipase CA: Novozym 435, a lipase (lipase B) from Can-
dida antarctica produced by submerged fermentation of a
genetically modified Aspergillus oryzae microorganism
and adsorbed on a macroporous acrylic resin, having
10,000 PLU g-1 (propyl laurate units: lipase activity based
on ester synthesis)] was kindly supplied by Novozymes
Japan, Ltd. (Chiba, Japan). The enzyme was dried under
vacuum (3 mmHg) over P2O5 at 25 �C for 2 h before use.
The purity and chemical structure of the synthetic com-
pounds were analyzed by thin-layer chromatography
(TLC), elemental analysis, and 1H nuclear magnetic reso-
nance (NMR) spectroscopy. TLC was carried out using
Merck silica gel 60 F254 plates (Merck Ltd., Darmstadt,
Germany). 1H NMR spectra were recorded with a Lambda
Fig. 1 Design of novel green
and sustainable gemini-type
cationics containing carbonate
linkages
388 J Surfact Deterg (2010) 13:387–398
123
300 Fourier Transform Spectrometer (JEOL Ltd., Tokyo,
Japan) operating at 300 MHz.
Preparation of n-Alkyl = N,N-
Dimethylaminoalkyl = Carbonate (CnX)
The n-alkyl = N,N-dimethylaminoalkyl = carbonate (CnX)
was prepared according to Scheme 1. The CnX was prepared
by the one-pot successive carbonate exchange reaction of
diphenyl carbonate 1 with 1-alkanol followed by reaction
with N,N-dimethylaminoalcohol in the presence of Et3N
according to previous work [23]. The molecular structure was
analyzed by 1H NMR spectroscopy and elemental analysis.
Their yield, the assignment of 1H NMR, and elemental
analysis are summarized in Table 1.
Preparation of Gemini-Type Cationics Containing
Carbonate Linkages in the Hydrophobic Moiety (GnX)
The gemini-type cationics, propane-1,3-bis(alkyl = N,N-
dimethylammoniumalkyl = carbonate) diiodide (GnX),
was prepared according to Scheme 1. GnX was prepared
by the reaction of CnX (0.44 mmol) and 1,3-diiodopropane
(0.20 mmol) in dry acetonitrile (2.0 mL) in a screw-capped
vial at 80 �C for 1 day with stirring. After the reaction, the
solvent was removed by evaporation under reduced pres-
sure to obtain the crude product. Purification was carried
out by recrystallization from ethyl acetate (1.0 mL) to
obtain the GnX in 68–86% yield as pale yellow crystals.
The molecular structure was analyzed by 1H NMR spec-
troscopy and elemental analysis. Their yield, melting point
Scheme 1 Synthesis and
chemical recycling of GnX
Table 1 Synthesis and analytical data of CnX
CnX Yield 1H NMR (300 MHz, CDCl3) C% H% N%
(%) d (ppm) Found Calcd. Found Calcd. Found Calcd.
C8Pr 91 0.88 (3H, t, J = 6.9 Hz), 1.20–1.42 (10H, m),
1.66 (2H, tt, J = 7.2, 7.5 Hz), 1.84 (2H,
tt, J = 7.2, 7.5 Hz), 2.23 (6H, s),
2.36 (2H, t, J = 7.5 Hz), 4.12 (2H, t,
J = 7.2 Hz), 4.18 (2H, t, J = 7.5 Hz)
64.68 64.83 11.21 11.27 5.40 5.40
C10Pr 85 0.88 (3H, t, J = 6.9 Hz), 1.19–1.42 (14H, m),
1.66 (2H, tt, J = 7.5, 7.5 Hz), 1.84 (2H, tt,
J = 7.5, 7.5 Hz), 2.23 (6H, s), 2.36 (2H, t,
J = 7.5 Hz), 4.12 (2H, t, J = 7.5 Hz),
4.18 (2H, t, J = 7.5 Hz)
66.68 66.86 11.27 11.57 4.96 4.87
C12Pr 91 0.88 (3H, t, J = 6.6 Hz), 1.17–1.41 (18H, m),
1.66 (2H, tt, J = 6.9, 6.9 Hz), 1.84 (2H, tt,
J = 7.2, 7.5 Hz), 2.23 (6H, s), 2.36 (2H, t,
J = 7.5 Hz), 4.12 (2H, t, J = 6.9 Hz),
4.18 (2H, t, J = 7.2 Hz)
68.36 68.53 11.69 11.82 4.40 4.44
C12iPr 75 0.88 (3H, t, J = 6.6 Hz), 1.17–1.43 (21H, m),
1.66 (2H, tt, J = 6.9, 6.9 Hz), 2.26 (6H, s),
2.27 (1H, dd, J = 6.0, 13.2 Hz), 2.56 (1H, dd,
J = 7.2, 13.2 Hz), 4.11 (2H, t, J = 6.9 Hz), 4.88 (1H, m)
68.49 68.53 11.78 11.82 4.41 4.44
J Surfact Deterg (2010) 13:387–398 389
123
(mp), the assignment of 1H NMR, and elemental analysis
are summarized in Table 2.
Preparation of Gemini-Type Cationics Containing
Carbonate Linkages in Both the Hydrophobic
and Linker Moieties (mG12Pr)
The gemini-type cationics containing carbonate linkages
both in the hydrophobic and linker moieties, 2G12Pr and
3G12Pr, were prepared by the reaction of C12Pr and
di(iodoalkyl) carbonate 3 according to Scheme 2.
Di(iodoalkyl) carbonate was prepared by the reaction of
diphenyl carbonate and iodoalkanol in the presence of
K2CO3 according to the previous report [24]. The 2G12Pr
was prepared by the reaction of C12Pr (0.22 mmol) and
di(2-iodoethyl) carbonate 3a (0.1 mmol) in acetonitrile
(1.0 mL) in a screw-capped vial at 80 �C for 3 days with
stirring. Purification was carried out by recrystallization
from ethyl acetate (1.0 mL) to obtain 2G12Pr in 74% yield
as a pale yellow crystal. In a similar procedure, 3G12Pr
was prepared using di(3-iodopropyl) carbonate 3b in 68%
yield as a pale yellow crystal. The molecular structure was
analyzed by 1H NMR spectroscopy and elemental analysis.
Their yield, mp, the assignment of 1H NMR, and elemental
analysis are summarized in Table 3.
Preparation of Single-Type Cationics Containing
Carbonate Linkages (S12X)
The quaternarization of C12X (1.0 mmol) was carried out
using methyl iodide (1.2 mmol) in dry acetonitrile
(1.0 mL) at room temperature for 30 min with stirring, as
shown in Scheme 3. After the reaction, the solvent and
unreacted methyl iodide were removed by evaporation
under reduced pressure to obtain the crude product. Puri-
fication was carried out by recrystallization from ethyl
acetate (3.0 mL) to obtain S12Pr in 85% yield as a white
crystal. In a similar procedure, S12iPr was prepared using
C12iPr in 87% yield as a white crystal. The molecular
structure was analyzed by 1H NMR spectroscopy and ele-
mental analysis. Their yield, mp, the assignment of 1H
NMR, and elemental analysis are summarized in Table 4.
Preparation of G12Pr-Derived Degradation Product
(3HPr)
In order to evaluate the biochemical oxygen demand
(BOD) biodegradability of the primary degradation prod-
ucts of G12Pr, propane-1,3-bis(N-3-hydroxypropyl-N,N-
dimethylammonium) diiodide (3HPr) was chemically
prepared. The 3HPr was prepared by the quaternarization
Table 2 Synthesis and analytical data of GnX
Cationics Yield mp 1H NMR (300 MHz, CDCl3) C% H% N%
(%) (�C) d (ppm) Found Calcd. Found Calcd. Found Calcd.
G8Pr 86 112–113 0.88 (6H, t, J = 6.6 Hz), 1.16–1.42
(20H, m), 1.67 (4H, tt, J = 6.9,
7.2 Hz), 2.26–2.42 (4H, m),
2.62–2.80 (2H, m), 3.47 (12H, s),
3.64–3.78 (4H, m), 3.88–4.01 (4H,
m), 4.13 (4H, t, J = 6.9 Hz), 4.30
(4H, t, J = 5.7 Hz)
45.90 45.70 7.98 7.92 3.43 3.44
G10Pr 79 125–127 0.88 (6H, t, J = 6.6 Hz), 1.18–1.42
(28H, m), 1.67 (4H, tt, J = 6.9,
7.2 Hz), 2.25–2.43 (4H, m),
2.62–2.80 (2H, m), 3.46 (12H, s),
3.63–3.78 (4H, m), 3.89–4.02 (4H,
m), 4.13 (4H, t, J = 6.9 Hz), 4.30
(4H, t, J = 5.9 Hz)
48.02 48.28 8.33 8.33 3.15 3.22
G12Pr 85 120–122 0.88 (6H, t, J = 6.6 Hz), 1.18–1.43
(36H, m), 1.67 (4H, tt, J = 7.2,
7.2 Hz), 2.26–2.42 (4H, m),
2.62–2.80 (2H, m), 3.46 (12H, s),
3.65–3.76 (4H, m), 3.89–4.01 (4H,
m), 4.13 (4H, t, J = 7.2 Hz), 4.30
(4H, t, J = 5.9 Hz)
50.28 50.54 8.56 8.70 2.97 3.02
G12iPr 68 128–130 0.88 (6H, t, J = 6.6 Hz), 1.18–1.43
(36H, m), 1.52 (3H, d, J = 6.0 Hz),
1.60–1.76 (4H, m), 2.68–3.02 (2H,
m), 3.38–3.62 (12H, m), 3.72–4.34
(12H, m), 5.21–5.38 (2H, m)
50.25 50.54 8.74 8.70 2.82 3.02
390 J Surfact Deterg (2010) 13:387–398
123
of 3-N,N-dimethylamino-1-propanol 4 (1.1 mmol) with
1,3-diiodopropane (0.5 mmol) in dry acetonitrile (1.0 mL)
in a screw-capped vial at 80 �C for 1 day with stirring, as
shown in Scheme 4. Purification was carried out by rep-
recipitation from methanol (1.0 mL, good solvent) and
ethyl acetate (3.0 mL, poor solvent) to obtain 3HPr in 83%
yield as a white crystal. The molecular structure was
confirmed by 1H NMR spectroscopy and elemental
analysis.
3HPr: 1H NMR (300 MHz, CD3OD): d = 2.02 (4H, tt,
J = 10.8, 11.7 Hz, N-CH2-CH2-), 2.30–2.46 (2H, m, N?-
CH2-CH2-CH2-N?), 3.23 (12H, s, 2N?(CH3)2), 3.44–3.61
(8H, m, 4N?-CH2-), 3.70 (4H, t, J = 6.6 Hz, 2-CH2-OH).
Anal. Calcd for C13H32N2O2I2 : C, 31.09; H, 6.42; N, 5.58.
Found: C, 31.31; H, 6.55; N, 5.52. mp 150–151 �C.
Hydrolytic Stability
Hydrolytic stability tests were carried out by dissolving
G12Pr and G12iPr at 5 g L-1 in distilled water and ace-
tate and phosphate buffers (pH 4.0 and 7.0, respectively) at
25 �C for 20 days. Hydrolytic degradation of gemini-type
cationics was analyzed by 1H NMR, and hydrolytic sta-
bility was calculated using the methylene protons adjacent
to the carbonate linkages at d 4.30 ppm of G12Pr and d5.21–5.38 ppm of G12iPr.
Scheme 3 Synthesis of S12X
Table 3 Synthesis and analytical data of mG12Pr
Cationics Yield mp 1H NMR (300 MHz, CDCl3) C% H% N%
(%) (�C) d (ppm) Found Calcd. Found Calcd. Found Calcd.
2G12Pr 74 131–133 0.88 (6H, t, J = 6.6 Hz), 1.18–1.41
(36H, m), 1.58–1.72 (4H, m),
2.20–2.36 (4H, m), 3.48 (12H, s),
3.78–3.91 (4H, m), 4.12 (4H, t,
J = 6.8 Hz) 4.30 (4H, t,
J = 5.6 Hz), 4.34–4.46 (4H, m),
4.86–5.00 (4H, m)
49.27 49.20 8.40 8.26 2.81 2.80
3G12Pr 68 158–159 0.88 (6H, t, J = 6.6 Hz), 1.20–1.42
(36H, m), 1.60–1.72 (4H, m),
2.22–2.37 (8H, m), 3.42 (12H, s),
3.64–3.76 (4H, m), 4.01–4.12 (4H,
m) 4.13 (4H, t, J = 7.1 Hz), 4.30
(4H, t, J = 6.0 Hz), 4.40 (4H, t,
J = 5.3 Hz)
49.88 50.19 8.44 8.42 2.67 2.72
Scheme 2 Synthesis of
di(iodoalkyl) carbonate as a
linker moiety and mG12Pr
J Surfact Deterg (2010) 13:387–398 391
123
Surfactant Properties
The static surface tension was measured using an automatic
digital Kyowa Precise Surface Tensiometer by the CBVP
method (Kyowa Kagaku Co. Ltd., Tokyo, Japan) at 25 �C. The
measurement was carried out using the Wilhelmy vertical plate
technique and a sandblasted glass plate. The test solutions were
aged at 25 �C for at least 1 h before any measurements.
The occupation area of a molecule at a surface (Amin)
was calculated according to the Gibbs adsorption equation.
The surface excess concentration (C) in mol m-2 and the
corresponding Amin in nm2 at the liquid/air interface were
calculated using Eqs. 1 and 2:
C ¼ �1
2:30nRT
dcdlogC
� �ð1Þ
Amin ¼1018
NACð2Þ
where n is a constant and depends upon the individual ions
comprising the surfactant (n = 2 for single-type cationics
and n = 3 for gemini-type cationics) [25, 26], dc/dlogC is
the slope of the surface tension versus concentration curves
below the CMC at a constant temperature, c is the surface
tension in mN m-1, T is the absolute temperature,
R = 8.31 (J mol-1 K-1), and NA is Avogadro’s number.
Biodegradabilities
The biodegradabilities of the cationic surfactants were
evaluated by BOD. The BOD was determined with a BOD
Tester (VELP Scientifica s.r.l., Usmate, MI, Italy) using the
oxygen consumption method according to the Modified
MITI Test [27]. Activated sludge was obtained from a
municipal sewage plant in Yokohama City, Japan. The
BOD-biodegradation (BOD/ThOD) was calculated from
the BOD values and the theoretical oxygen demand
(ThOD).
Enzymatic Degradation and Reproduction for Chemical
Recycling
The enzymatic degradation of gemini-type cationics
containing carbonate linkages was carried out using
immobilized lipase. The enzymatic degradation of
G12Pr (50 mg) was carried out using 100 wt% immo-
bilized lipase CA (50 mg) in toluene (1.0 mL) and H2O
(10 lL) at 65 �C for 3 days with stirring, as shown in
Scheme 1. After the reaction, the immobilized lipase
CA was removed by filtration, and the solvent was
evaporated under reduced pressure. Purification was
carried out by reprecipitation using methanol (0.2 mL,
good solvent) and ethyl acetate (1.0 mL, poor solvent)
to obtain the corresponding quaternary ammonium
alcohol (3HPr) in 92% yield. The molecular structure
of the degradation products was analyzed by 1H NMR
spectroscopy.
The regeneration of G12Pr was carried out using the
degradation products and diphenyl carbonate. That is, a
mixture of 3HPr (20.5 mg), 1-dodecyl = phenyl = car-
bonate (50.0 mg) and immobilized lipase CA (5.0 mg) in
dry acetonitrile (1.0 mL) was stirred at 40 �C for 4 days.
After the reaction, the immobilized lipase CA was
removed by filtration and the solvent was evaporated
under reduced pressure to obtain the crude product.
Purification was carried out by recrystallization from
ethyl acetate (1.0 mL) to obtain the G12Pr in 35% yield.
The molecular structure was confirmed by 1H NMR
spectroscopy.
Scheme 4 Synthesis of G12Pr-derived 3HPr
Table 4 Synthesis and analytical data of S12X
Cationics Yield mp 1H NMR (300 MHz, CDCl3) C% H% N%
(%) (�C) d (ppm) Found Calcd. Found Calcd. Found Calcd.
S12Pr 85 115–117 0.88 (3H, t, J = 6.6 Hz), 1.19–1.42 (18H,
m), 1.67 (2H, tt, J = 6.9, 6.9 Hz),
2.21–2.33 (2H, m), 3.53 (9H, s),
3.73–3.84 (2H, m), 4.14 (2H, t,
J = 6.9 Hz), 4.30 (2H, t, J = 6.0) Hz)
49.76 49.89 8.68 8.81 3.07 3.06
S12iPr 87 141–142 0.88 (3H, t, J = 6.6 Hz), 1.18–1.43 (18H,
m), 1.48 (3H, d, J = 6.9 Hz), 1.67 (2H,
tt, J = 6.9, 6.9 Hz), 3.54 (9H, s), 3.59
(1H, dd, J = 9.9, 14.1 Hz), 4.09–4.25
(2H, m), 4.57 (1H, d, J = 14.1 Hz),
5.25–5.37 (1H, m)
49.73 49.89 8.71 8.81 2.93 3.06
392 J Surfact Deterg (2010) 13:387–398
123
Antimicrobial Activities
The antimicrobial activities of the surfactants were
evaluated by the agar dilution method [28]. Gram-posi-
tive bacterial strains (Staphylococcus aureus KB210,
Bacillus subtilis KB211, and Micrococcus luteus KB212),
gram-negative bacterial strains (Escherichia coli KB213,
Salmonella typhimurium KB20, and Pseudomonas aeru-
ginosa KB115), six fungal strains (Candida albicans
KF1, Saccharomyces cerevisiae KF25, Trichophyton
mentagrophytes KF213, Microsporum gypseum KF64,
Penicillium chrysogenum KF270, and Aspergillus niger
KF103) were used. Nutrient agar and Sabouraud dextrose
agar were used for the bacteria and fungi, respectively.
The antimicrobial activity was expressed as the minimum
inhibitory concentration (MIC).
Results and Discussion
Synthesis of Gemini-Type Cationics Containing
Carbonate Linkages
The CnX was prepared in a one-pot two-step successive
reaction according to our previous report [23]. That is,
CnX was first prepared by the reaction of diphenyl car-
bonate and 1-alkanol in the presence of Et3N followed by
the reaction of N,N-dimethylaminoalcohol in a one-pot
two-step reaction procedure, as shown in Scheme 1.
Simultaneous quaternarization and gemini formation
readily occurred at 80 �C for 1 day by the reaction with
CnX and 1,3-diiodopropane in dry acetonitrile to produce
GnX containing a carbonate linkage in the hydrophobic
moiety in 68–86% yield. The yield of G12Pr was 66%
when the concentration of 1,3-diiodopropane was
0.2 mol L-1. On the other hand, its yield was 85% when
the concentration of 1,3-diiodopropane was 0.1 mol L-1.
These results implied that the solubility of G12Pr was
relatively low in acetonitrile. mG12Pr containing carbon-
ate linkages both in hydrophobic and linker moieties was
prepared at 80 �C for 3 days by the reaction with CnX and
a,x-diiodide containing a carbonate linkage (3) in 68–74%
yield. In a 1-day reaction, the yield of 2G12Pr was only
20%. The maximum yield was 74% when the reaction time
was 3 days. This could be due to the lower reactivity of the
larger molecular size of di(iodoalkyl) carbonate. The
gemini-type cationics containing carbonate linkage only in
the linker moiety was prepared using dry ethyl acetate [24].
On the other hand, GnX and mG12Pr containing carbon-
ate linkages in the hydrophobic moiety were prepared in
dry acetonitrile due to the low solubility of mG12Pr in
ethyl acetate.
Hydrolytic Stability
In this study, a hydrolytic degradation test was carried out
by dissolving G12Pr and G12iPr in distilled water and
acetate and phosphate buffers (pH 4.0 and 7.0, respec-
tively) at 25 �C. It was found that both G12Pr and G12iPr
were stable in distilled water. Only a slight degradation
occurred after 20 days of incubation; the remaining car-
bonate was 98% for G12Pr and 97% for G12iPr. Figure 2
shows the time course of the hydrolytic degradation of
gemini-type cationics as measured by 1H NMR. G12iPr
was hydrolyzed faster at pH 7.0 in phosphate buffer com-
pared to pH 4.0 in acetate buffer. On the other hand,
G12Pr was practically stable at both pH 4.0 and 7.0. It is
reported that the hydrolysis of cationics having an ester
linkage in the vicinity of the polar hydrophilic groups was
influenced by the adjacent electron-withdrawing or elec-
tron-donating groups [19]. The G12Pr was hydrolytically
more stable in tested buffers when compared to G12iPr.
The higher hydrolyzability of G12iPr was due to the lower
electron density of the carbonyl carbon. Figure 3 shows the1H NMR spectra of G12Pr and G12iPr. Significant dif-
ferences in the chemical shift of the methylene protons
Fig. 2 Time course of
hydrolytic degradation of the
G12Pr and G12iPr in buffers at
25 �C. a G12Pr (open circles)
and G12iPr (filled circles) in
acetate buffer (pH 4.0).
b G12Pr (open circles) and
G12iPr (filled circles) in
phosphate buffer (pH 7.0).
Sample concentration: 5 g L-1
J Surfact Deterg (2010) 13:387–398 393
123
adjacent to the carbonate linkages were observed between
G12Pr [d 4.30 ppm (e in Fig. 3a)] and G12iPr [d5.21–5.38 ppm (e’ in Fig. 3b)]. These results implied that
the electron density of the carbonyl carbon of G12iPr was
lower than the electron density of the carbonyl carbon of
G12Pr. The distance between the carbonate linkage and
the quaternary ammonium group of G12iPr is shorter than
that of G12Pr. Therefore, the carbonyl carbon of G12iPr
was affected more by the positive charge of the quaternary
ammonium group than that of G12Pr.
Surfactant Properties of Gemini-Type Cationics
Containing Carbonate Linkages in Aqueous Solution
Figure 4 shows the plots of surface tension versus con-
centration of gemini-type cationics containing carbonate
linkages in aqueous solution. From these plots, the CMC,
the surface tension at the CMC values (cCMC), the effi-
ciency of adsorption at the surface (pC20) [pC20, the neg-
ative log of C20, the surfactant molar concentration
required to reduce surface tension by 20 mN m-1] [29,
Fig. 3 1H NMR spectra of
G12Pr (a) and G12iPr (b) in
CDCl3
394 J Surfact Deterg (2010) 13:387–398
123
30], and the Amin of gemini-type and single-type cationics
were determined and are listed in Table 5. It was found that
gemini-type cationics containing carbonate linkages
showed lower CMC values compared to the corresponding
single-type cationics. These low CMC values of gemini-
type surfactants were mainly caused by the simultaneous
migration of the two alkyl chains, rather than one, from the
aqueous phase to the micelle [31–33]. No significant dif-
ferences in the CMC values of the tested gemini-type
cationics containing both the carbonate linkages and
n-dodecyl groups were observed according to the linker
structure. It was also found that G12X showed lower cCMC
values when compared to the corresponding single-type
S12X. The cCMC of 3G12Pr was slightly higher than that
of 2G12Pr. This is due to the difference in the linker length
between the quaternary ammonium groups. That is, the
2G12Pr having an ethoxycarbonyloxyethyl-type linker
(m = 2 in Fig. 1) showed a lower cCMC value when com-
pared to the corresponding 3G12Pr having a propoxy-
carbonyloxypropyl-type linker (m = 3). The lower cCMC of
2G12Pr was due to the higher intra- and intermolecular
hydrophobic interactions between the two hydrophobic
alkyl chains of the gemini-type surfactant. This is also
supported by the results that the Amin of the 2G12Pr was
smaller than that of 3G12Pr. Furthermore, the pC20 values
of the gemini-type cationics containing carbonate linkages
were higher than those of the corresponding single-type
cationics. That is, the gemini-type cationics containing
carbonate linkages adsorb more efficiently at the surface
than the corresponding single-type cationics.
Biodegradabilities
The quick and complete biodegradation of surfactants after
use is needed in terms of the establishment of green and
sustainable chemistry, because water-soluble household
detergents are generally difficult to recover or reuse. The
biodegradation of the synthetic gemini-type cationics
containing carbonate linkages first occurs at enzymatically
hydrolyzable carbonate linkages by environmental
microbes with the evolution of carbon dioxide to form low-
molecular-weight fragments. Further microbial assimilation
of primary degradation products then follows [22]. If such
degradation products are biodegradable, the parent surfac-
tants can be regarded as biodegradable.
Figure 5 shows the BOD-biodegradation (BOD/
ThOD 9 100) of gemini-type cationics and the G12Pr-
derived degradation products [quaternary ammonium
alcohol: 3HPr and 1-dodecanol (DD) shown in Scheme 1].
The single-type cationics containing carbonate linkages,
S12Pr, was biodegraded by the activated sludge, and its
BOD-biodegradability exceeded 60% after a 45-day incu-
bation. The conventional gemini-type cationics, G12,
which had no hydrolytically cleavable moiety, showed no
biodegradation by activated sludge. On the other hand, the
G12X containing carbonate linkages showed higher bio-
degradability when compared to the conventional G12. It
was found that the biodegradability was improved by the
introduction of carbonate linkages into the hydrophobic
moiety of the gemini-type cationics. However, the biode-
gradability of G12Pr was relatively low at around 25%
Fig. 4 Surface tension versus concentration of gemini-type cationics containing carbonate linkages in aqueous solution at 25 �C. a G8Pr (opencircles); G10Pr (filled circles); G12Pr (open squares). b 2G12Pr (open circles); 3G12Pr (filled circles). c G12iPr (open circles)
Table 5 Surfactant properties of gemini-type and single-type
cationics in aqueous solution at 25 �C
Cationics CMC (mM) cCMC
(mN m-1)
pC20 102 Amin
(nm2)
G8Pr 0.948 32.2 3.6 81.2
G10Pr 0.146 30.4 4.6 99.6
G12Pr 0.0578 30.8 5.2 118
2G12Pr 0.0401 33.9 5.1 107
3G12Pr 0.0571 36.7 5.2 162
G12iPr 0.0254 33.2 5.5 127
G12 0.165 30.7 4.3 66.7
S12Pr 0.431 32.8 4.0 60.1
S12iPr 1.29 34.7 3.6 73.5
J Surfact Deterg (2010) 13:387–398 395
123
after 28 days of incubation. This is due to the relatively
low biodegradability of 3HPr as the primary biodegrada-
tion intermediate, i.e., 10% BOD-biodegradation after
28 days, as shown in Fig. 5. On the other hand, 1-dodec-
anol as the degradation intermediate was readily biode-
graded by activated sludge, and its BOD-biodegradability
exceeded 60% after 28 days. Based on these results, the
low biodegradability of G12Pr was due to the low biode-
gradability of the degradation intermediates having two
ammonium groups, 3HPr.
The biodegradability of gemini-type cationics containing
carbonate linkages was influenced by the linker structure.
Though the 2G12Pr was quickly biodegraded, the 3G12Pr
showed relatively low biodegradability. This is due to the
difference in the primary degradation products. In order to
compare the hydrolytic degradability of 2G12Pr and
3G12Pr, an accelerated hydrolytic degradation test was
carried out by dissolving the gemini-type cationics at
5 g L-1 in distilled water and stirring at a higher temperature
of 60 �C. The hydrolytic degradation of 2G12Pr was ana-
lyzed by comparing the 1H NMR profiles of the reactants
before and after the degradation, and the results are shown in
Fig. 6a. Significant differences in the hydrolytic degradation
were observed depending on whether the carbonate linkage
was in the linker moiety or the hydrophobic moiety of the
2G12Pr. The carbonate linkage in the linker moiety gradu-
ally hydrolyzed in water, and only 18% remained after 9 h of
reaction. On the other hand, 97% of the carbonate linkage in
the hydrophobic moiety remained after 9 h. These results
indicated that the carbonate linkage in the hydrophobic
moiety was more stable against hydrolysis than the carbonate
linkage in the linker moiety. Therefore, 2G12Pr was readily
hydrolyzed at the carbonate linkage in the linker moiety to
produce the corresponding quaternary ammonium alcohols
having a similar molecular structure to the single-type
S12Pr, which exhibited good biodegradability.
Next, 1H NMR profiles before and after the hydrolysis
of 3G12Pr were analyzed. The results are shown in
Fig. 6b. The carbonate linkage in the linker moiety was
stable in water, and 95% of the carbonate linkage remained
after 9 h at 60 �C. Also, 96% of the carbonate linkage in
the hydrophobic moiety remained after the hydrolysis. It
was found that the carbonate linkage in the linker moiety of
3G12Pr was hydrolytically more stable than the carbonate
linkage in the linker moiety of 2G12Pr. Based on these
results, 2G12Pr was readily cleaved at the carbonate
linkage in the linker moiety, indicating a higher degree of
BOD-biodegradability than 3G12Pr.
Enzymatic Degradation and Reproduction for Chemical
Recycling
In terms of green and sustainable chemistry, even water-
soluble surfactants should be chemically recycled, partic-
ularly in industrial fields. Gemini-type cationics containing
carbonate linkages were hydrolyzed by lipase and accom-
panied by carbon dioxide evolution to produce the corre-
sponding alcohol and quaternary ammonium alkanol,
which could be converted into the initial gemini-type
Fig. 5 BOD-biodegradability of gemini-type and single-type cation-
ics containing carbonate linkages and G12Pr-derived degradation
products, 3HPr and DD, at 25 �C for 28 days (*45 days). Activated
sludge: 30 ppm; sample concentration: ca. 40 ppm
Fig. 6 Time course of
hydrolytic degradation of
mG12Pr in distilled water at
60 �C. a Remaining carbonate
in the hydrophobic moiety
(open circles) and linker moiety
(filled circles) of 2G12Pr.
b Remaining carbonate in the
hydrophobic moiety (opencircles) and linker moiety (filledcircles) of 3G12Pr. Sample
concentration: 5 g L-1
396 J Surfact Deterg (2010) 13:387–398
123
cationics by the reaction with diphenyl carbonate. A lipase-
catalyzed chemical recycling procedure may become a
green method because lipase is a renewable catalyst with
high catalytic activities.
The enzymatic degradation of G12X was carried out in
toluene containing a small amount of water using immo-
bilized lipase CA. The G12Pr was degraded at the car-
bonate linkage into the quaternary ammonium alcohol
(3HPr) and 1-dodecanol, as shown in Scheme 1. The
G12Pr was regenerated by the reaction of 3HPr and
1-dodecyl = phenyl = carbonate, which was prepared by
the Et3N-catalyzed reaction of 1-dodecanol and diphenyl
carbonate (78% yield). That is, a mixture of 3HPr,
1-dodecyl = phenyl = carbonate, and immobilized lipase
CA was stirred in dry acetonitrile to obtain G12Pr. Based
on these results, G12Pr showed chemical recyclability
using lipase CA. On the other hand, the G12iPr was not
quickly degraded by lipase under similar conditions. The
lower enzymatic degradability of G12iPr was due to the
steric hindrance of the side methyl group.
Antimicrobial Activities
The gemini-type cationics were screened for their antimi-
crobial activities toward gram-positive and gram-negative
bacterial strains and fungal strains based on the determi-
nation of their MICs [28]. These results are shown in
Table 6. The MIC value shows the lowest concentration of
a surfactant at which the tested microorganisms do not
show visible growth. It is reported that cationic surfactants
having multi-polar groups showed higher antimicrobial
activities compared to the corresponding single-type cat-
ionics because of the much higher charge density carried
by multi-polar cationics [34, 35]. However, G12X showed
lower antimicrobial activities when compared to the cor-
responding single-type S12X. The low antimicrobial
activities of G12Pr could be due to the ready cleavability
of the carbonate linkages of G12Pr by microbes forming
surface-inactive compounds, 3HPr, as shown in Scheme 1.
The 2G12Pr containing carbonate linkages both in the
hydrophobic and linker moieties showed higher antimi-
crobial activities than the 3G12Pr. As discussed above,
2G12Pr was readily hydrolyzed at the carbonate linkage in
the linker moiety to produce the corresponding quaternary
ammonium alcohols having a similar molecular structure to
the single-type S12Pr, which exhibited strong antimicro-
bial activities. On the other hand, 3G12Pr could be cleaved
at the carbonate linkages in both the hydrophobic and
linker moieties to produce the antimicrobially inactive
alkyl chain-free fragments. Therefore, the antimicrobial
activities of 3G12Pr were lower than those of 2G12Pr.
Acknowledgments Immobilized lipase from Candida antarctica(lipase CA, Novozym 435) was kindly supplied by Novozymes Japan
Ltd. (Chiba, Japan). This work was supported by a Grant-in-Aid for
JSPS Fellows 21�4882 from the Ministry of Education, Culture,
Sports, Science and Technology (MEXT), Japan. This work was also
supported by the High-Tech Research Center Project for Private
Universities, matching the fund subsidy from the MEXT, 2006–2011.
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Author Biographies
Taisuke Banno is a Ph.D. student at Keio University, Japan. His main
interests are the synthesis, physicochemical properties, biodegrada-
tion, and chemical recycling of green gemini-type surfactants.
Kazuo Kawada received his Ph.D. in the synthesis and physico-
chemical properties and microbial properties of nonionic surfactants
from Keio University. He is currently an assistant professor of the
Department of Chemistry, School of Science, Kitasato University. His
main research interests are the synthesis and evaluation of antimi-
crobial agents and surfactants.
Shuichi Matsumura earned a Ph.D. and is currently a professor of
the Department of Applied Chemistry, Keio University. His research
program focuses on the development of novel enzyme-catalyzed
polymerization for the establishment of green chemistry, sustainable
chemical recycling of green and bio-based plastics using an enzyme,
and new biodegradable surfactants and detergent builders.
398 J Surfact Deterg (2010) 13:387–398
123
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