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Environmental and Health Assessment of Substances in Household Detergents and
Cosmetic Detergent Products
Surface-active compounds with both acidic and alkaline properties are known as amphoteric
surfactants. Amphoteric surfactants include two main groups, i.e. betaines and real
amphoteric surfactants based on fatty alkyl imidazolines. The key functional groups in the
chemical structures are the more or less quaternized nitrogen and the carboxylic group.
Betaines are characterized by a fully quaternized nitrogen atom and do not exhibit anionic
properties in alkaline solutions, which means that betaines are present only as
zwitterions. Another group of amphoterics is designated imidazoline
derivatives because of the formation of an intermediate imidazoline structure during the
synthesis of some of these surfactants. This group contains the real amphoteric
surfactants that form cations in acidic solutions, anions in alkaline solutions, and
zwitterions in mid-pH range solutions. The mid-pH range (isoelectric range) in
which the surfactant has a neutral charge is compound specific and depends on the
alkalinity of the nitrogen atom and the acidity of the carboxylic group (Domsch 1995).
Amphoteric surfactants are used in personal care products (e.g. hair shampoos and
conditioners, liquid soaps, and cleansing lotions) and in all-purpose and industrial
cleaning agents. The total volume of amphoteric surfactants consumed in commercial
products today is relatively small (see Chapter 2), but the consumption of these chemicals
is expected to increase in the future because of the request for milder surfactants.
Besides acting as mild surfactants, the amphoterics may improve the mildness of especially
anionic surfactants. By volume, the most important groups of amphoteric surfactants today
consist of alkylamido betaines and alkyl betaines. The use of alkylamphoacetates in
personal care products is expected to grow in coming years.
Betaines are primarily used in personal care products like, e.g. hair shampoos,
liquid soaps, and cleansing lotions. Other applications include all-purpose cleaning
agents, hand dishwashing agents, and special textile detergents. All betaines are
characterized by a fully quaternized nitrogen. In alkyl betaines, one of the methyl groups
in the betaine structure (N,N,N-trimethylglycine) is replaced by a
linear alkyl chain. A special type of betaines is the hydroxysulfobetaines in which the
carboxylic group of alkyl betaine is replaced by sulfonate and a hydroxy-group is inserted
in the hydrophilic part of the molecule. In alkylamido betaines, an amide group is
inserted as a link between the hydrophobic alkyl chain and the hydrophilic moiety. The
most commonly used alkylamido betaine is alkylamidopropyl betaine (e.g., cocoamidopropyl
betaine), whereas alkylamidoethyl betaines are used in smaller amounts.
Representative structures of betaines are shown below.

No data were found on the occurrence of betaines in the environment.
Aerobic biodegradability
The primary biodegradability of betaines approaches 100% as, e.g., the loss of
surface-activity attained 100% for C12 alkyl betaine, 98% for cocoamidopropyl
betaine, and 96 and 100% for C14-15 hydroxysulfobetaine (Domsch 1995, and
references therein). The results from ultimate biodegradability tests of alkyl betaines
show some variation with degradation percentages below and above the pass level for ready
biodegradability, especially if older data of Fernlay (1978, cited in Domsch 1995) are
taken into account. However, both alkyl betaines and cocoalkylamido betaines can be
regarded as readily biodegradable on the basis of the data in Table 6.1. The
hydroxysulfobetaines are probably not readily biodegradable in standard screening tests as
indicated by a biodegradability of 40 and 47% of ThOD in the closed bottle test (Table
6.1).
Table 6.1
Ultimate aerobic biodegradability of betaines.
Compound |
Test |
Result |
Reference |
C12-14 alkyl betaine |
Closed bottle test, 28 d |
63% ThOD |
Madsen et al. 1994 |
C12-18 alkyl betaine |
Closed bottle test, 28 d |
> 60% ThOD |
Brøste 1998 |
Cocoalkyl betaine |
Closed bottle test, 30 d |
> 60% ThOD |
Domsch 1995 |
Cocoalkyl betaine |
Closed bottle test, 30 d |
57% ThOD |
Domsch 1995 |
Cocoalkyl amidopropyl betaine |
Closed bottle test, 30 d |
84% ThOD |
IUCLID 2000 |
Cocoalkyl amidopropyl betaine |
Modified OECD screening test, 28 d |
100% DOC |
IUCLID 2000 |
Cocoalkyl amidopropyl betaine |
Modified OECD screening test |
90-94% DOC |
Domsch 1995 |
C14-15 hydroxysulfo betaine |
Closed bottle test |
40% ThOD |
Domsch 1995 |
Cocoalkyl hydroxysulfo betaine |
Closed bottle test |
47% ThOD |
Domsch 1995 |
Anaerobic biodegradability
The knowledge about the biodegradability of betaines under anoxic conditions is
relatively scarce. A search in the literature by Goldschmidt (1993-1994) indicates that
sulfate-reducing marine bacteria belonging to the genus Desulfobacterium are able
to grow on betaine with the stoichiometric formation of N,N-dimethylglycine
(Heijthuijsen and Hansen 1989, cited in Goldschmidt 1993-1994). Another study indicated
that betaine was anaerobically degraded to methylamine in sewage sludge at a betaine
concentration of 2 g/l and a solids concentration of 3.3 g/l (Gwardys and
Nowakowska-Waszczuk 1981, cited in Goldschmidt 1993-1994). The anaerobic biodegradability
of cocoamidopropyl betaine was examined in the present study by using the ISO 11734
screening test. Under the methanogenic test conditions, the ultimate biodegradability of
cocoamidopropyl betaine attained 45 and 75% of ThGP after 28 and 56 days, respectively, at
the applied test concentration of 14.4 mg C/l (Appendix; Table A14, Figure A14).
Bioaccumulation
No experimental data describing the bioaccumulation potential of betaines were found in
the literature.
The aquatic toxicity of betaines varies considerably, even within the same species,
which is particularly evident by evaluating the EC50 values determined for the green alga Scenedesmus
subspicatus. For this species, the EC50 obtained in tests with cocoamidopropyl betaine
are between 0.55 and 48 mg/l. The geometric mean of the EC50 obtained for S.
subspicatus is 3.1 mg/l, when the values 0.55, 1.84, and 30 mg/l are used (Table 6.2).
The EC/LC50 of alkyl and cocoamidopropyl betaines towards crustaceans and fish are between
1 and 100 mg/l.
Table 6.2
Effects of alkyl and alkylamidopropyl betaines to aquatic organisms.
Species |
Surfactant |
EC/LC50 (mg/l) |
Duration |
Reference |
Algae |
C12-14 alkyl betaine |
2.5 |
72 h |
Berol Nobel 1993 |
Algae
(Scenedesmus subspicatus) |
Cocoamidopropyl betaine |
1.84 |
72 h |
IUCLID 2000 |
Algae
(Scenedesmus subspicatus) |
Cocoamidopropyl betaine |
Growth rate:
0.55
NOEC: 0.09 |
96 h |
IUCLID 2000 |
Algae
(Scenedesmus subspicatus) |
Cocoamidopropyl betaine |
Biomass:
30; 33
NOEC: 3.2
Growth rate:
45; 48
NOEC: 3.2; 10 |
72 h |
Goldschmidt 1993-1994 |
Daphnia magna |
Cocoamidopropyl betaine |
6.5
NOEC:
1.6 |
48 h |
IUCLID 2000 |
Daphnia magna |
Cocoamidopropyl betaine |
21.7 |
48 h |
IUCLID 2000 |
Zebra fish
(Brachydanio rerio) |
C12-14 alkyl betaine |
21.9 |
96 h |
Berol Nobel 1993 |
Fish |
C12-18 alkyl betaine |
10-100 |
- |
Brøste 1998 |
Zebra fish
(Brachydanio rerio) |
Cocoamidopropyl betaine |
2.0
NOEC: 1.7 |
96 h |
IUCLID 2000 |
Toxicokinetics and acute toxicity
Amphoteric surfactants are easily absorbed in the intestine and are excreted partly
unchanged via the faeces. Metabolization to CO2 and short-chained fatty acids
also occur. No tendency to accumulation in the organism or storage of betaines in certain
organs has been detected (SFT 1991). Betaines generally have a low acute toxicity. E.g.,
LD50 values for cocoamidopropylbetain (30% solution) by oral administration have been
determined to 4,910 mg/kg body weight in rats (CIRP 1991a).
Skin and eye irritation
Betaines do not carry any net charge, and, therefore, they can only form hydrophobic
bonds with proteins in the skin. This may be the explanation for the low protein
denaturation potential of betaines as the ion-binding of other surfactants contributes to
denaturation. In combination with anionic surfactants a positive synergistic effect with
regard to skin compatibility is often found. Compared to a 20% solution of C12
alkyl sulfate (AS; sodium lauryl sulfate) alone, decreased erythema was observed for the
combination of 20% C12 AS and 10% cocoamidopropyl betaine one hour after the
removal of patches (Dillarstone and Paye 1993). The combination of cocoamidopropyl betaine
and C12 AS also reduced swelling of the skin, and generally interactions
between amphoterics and AS produce less swelling and result in milder skin reactions
(Rhein et al. 1986).
Concentrated betaines are expected to be irritant to skin and eyes. Diluted solutions
(3-10%) are not irritant to skin, but they are mildly irritant to the eyes (4.5%) (KEMI
1994).
Solutions containing 7.5% and 10% cocoamidopropyl betaine were not irritating to intact
or abraded rabbit skin in a single insult occlusive patch test. The PII (Primary
Irritation Index) for the solution was < 0.3 (maximum score is 8). When a 15%
solution was tested under occlusive patches for 24 hours by using the same procedure, a
PII of 3.5 was achieved and well-defined erythema and edema were observed (CIRP 1991a).
In a Draize test for ocular irritation a concentration of 4.5% cocoamidopropyl betaine
produced a slight conjunctival irritation (erythema and swelling of conjunctiva) in
unrinsed eyes and a very slight conjunctival irritation in rinsed eyes of rabbits. The
surfactant was instilled into the conjunctival sac of the eye. No corneal involvement or
iris congestion was seen (CIRP 1991a). The maximum mean irritation scores for eyes of
rabbits treated with 30% cocoamidopropyl betaine and left unrinsed were in the range
between 26 and 42 (maximum score is 110) (CIRP 1991a).
Sensitization
No evidence of delayed contact hypersensitivity was found in guinea pigs after
topically administrated solutions of 10% cocoamidopropyl betaine by using the
Magnusson-Kligman maximization test (CIRP 1991a). Various instances of contact allergy to
cocoamidopropyl betaine have been reported. In all of the reports it was concluded that
the observed skin reactions were due to the presence of 3-dimethylaminopropylamine which
is an impurity in cocoamidopropyl betaine. This impurity is an intermediate in the
synthesis of alkylamidopropyldimethylamines that are intermediates in the synthesis of the
corresponding alkylamido betaines (Angelini et al. 1995, 1996a, 1996b; Armstrong et
al. 1999).
Mutagenicity
Cocoamidopropyl betaine was proven to be non-mutagenic to Salmonella typhimurium
in the Ames Salmonella/microsome reverse mutation assay (CIRP 1991a). Short-term
genotoxicity tests have shown negative results of mutagenicity for lauryl betaine in
various strains of Salmonella typhimurium (Yam et al. 1984).
No tests on reproductive toxicity and carcinogenicity were available.
Classification
Betaines are not included in Annex 1 of list of dangerous substances of Council
Directive 67/548/EEC.
The amphoteric surfactants in this group include structures designated as
alkylamphoacetates, alkylamphopropionates, and alkyliminopropionates. These surfactants
are usually produced by the reaction of fatty acids or their esters with amines (e.g.
aminoethylethanol amine). Alkylamphopropionates may be obtained by the addition of acrylic
acid, methyl acrylate, or ethyl acrylate to the reaction product of fatty acids and
amines. During the synthesis of most of the surfactants an intermediate imidazoline ring
structure may be formed (hence the common name imidazoline derivatives). The
imidazoline ring is probably opened by the influence of hydrolysing conditions and does
not appear in the final products (Domsch 1995). Alkylamphoacetates, alkylamphopropionates,
and alkyliminopropionates are used in products like hair shampoos, liquid soaps, and
shower gels. Other major applications of alkylamphopropionates and alkyliminopropionates
include highly acidic and alkaline household cleaning agents. Commercial products may
contain complex mixtures of the amphoteric surfactants described in this section.
Representative structures are given below.

No data were found on the occurrence of these amphoteric surfactants in the
environment.
Aerbic biodegradability
The ultimate aerobic biodegradability of alkylamphodiacetates, alkylamphopropionate,
and alkyliminodipropionate complies with the pass levels for ready biodegradability in
OECD 301 screening tests (Table 6.3).
Table 6.3
Ultimate aerobic biodegradability of amphoteric imidazoline derivatives.
Compound |
Test |
Result |
Reference |
Cocoamphodiacetate |
Closed bottle test, 30 d |
> 60%; 66% ThOD |
Domsch 1995 |
Cocoamphodiacetate |
Modified OECD screening test |
> 70% DOC |
Domsch 1995 |
C12-18 alkylampho-propionate |
Modified OECD screening test |
79% ThOD |
Domsch 1995 |
C12 alkylimino-dipropionate |
Manometric respirometry test, 28 d |
99% ThOD |
This study (Appendix; Table A3, Figure
A3) |
Anaerobic biodegradability
Information on the ultimate anaerobic biodegradability of imidazoline derivatives has
not been found in the literature. The anaerobic biodegradability of C12
alkyliminodipropinate (16.4 mg C/l) reached only 2.5% of ThGP during 56 days in the ISO
11734 screening test which was performed in the present study. However, the test substrate
concentration inhibited the anaerobic bacteria, and inhibitory effects may have precluded
biodegradation (Appendix; Table A15, Figure A15).
Bioaccumulation
No experimental data describing the bioaccumulation potential of alkylamphoacetates,
alkylamphopropionates, or alkyliminopropionates were found in the literature.
Acute toxicity
No data describing the aquatic toxicity of the amphoteric surfactants in this group
were found in the literature. Because of the variability in the effect concentrations
observed for betaines (see Table 6.2), it is not tempting to base the assessment upon
structural analogy and betaine aquatic toxicity. Testing of the aquatic toxicity and the
subsequent release of data to the open literature should be encouraged as the consumption
of these surfactants is expected to increase.
Alkylamphoacetates and akylamphopropionates have a low acute toxicity after oral
administration to rats (Table 6.4).
Table 6.4
Acute toxicity (LD50) of amphoteric surfactants by oral administration.
Surfactant |
Species |
LD50 (g/kg body weight) |
Reference |
Cocoamphoacetate |
Rat |
15.9 28 ml |
CIRP 1990 |
Cocoamphodiacetate |
Rat |
> 5.0 16.6 |
CIRP 1990 |
Cocoamphopropionate |
Rat |
20.0 ml* |
CIRP 1990 |
Cocoamphodipropionate |
Rat |
> 5.0 16.3 |
CIRP 1990 |
* Commercial solution in water, probably 40-50%.
Skin and eye irritation
Generally these amphoteric surfactants do not seem to be irritant to the skin and only
to a small extent irritating to the eye (SFT 1991). Some variation in test results have
been reported.
Cocoamphodipropionate was found to be non-irritating as a concentration of 7.5-70% (PII
= 0), whereas cocoamphopropionate was slightly irritating to rabbit skin at a
concentration of 1516%. Cocoamphodiacetate was non-irritating to slightly irritating
at a concentration of 10-12% (CIRP 1990).
A Draize test has shown that cocoamphodipropionate was practically non-irritating to
the eye at a concentration of 7.5%, whereas cocoamphopropionate was non-irritating to
slightly irritating at 5% and 16%. Cocoamphodiacetate was moderately to severely
irritating to the eye at a concentration of 10-12%. Cocoamphoacetate was slightly to
severely irritating at 16 to 50% (CIRP 1990).
Sensitization
Cocoamphoacetate and cocoamphopropionate were non-irritating and non-sensitizing in a
repeated insult patch test (non-occlusive) involving 141 subjects. The concentration of
the surfactants was 10% in distilled water. During induction, each chemical was applied to
the back three times per week for three weeks. The challenge phase was initiated 10 to 15
days after application of the final induction patch. Cocoamphoacetate and
cocoamphopropionate did not induce sensitization in any of the subjects (CIRP 1990).
Cocoamphoacetate was non-sensitizing in guinea pigs when tested in the Magnusson-Kligman
maximization test. The tested concentrations for induction and challenge were 25, 50 and
100% (CIRP 1990).
Mutagenicity
Cocoamphodiacetate, cocoamphopropionate, and cocoamphodipropionate were non-mutagenic,
when evaluated in the Ames Salmonella/microsome assay using different strains of Salmonella
typhimurium (CIRP 1990).
No tests on reproductive toxicity and carcinogenicity were available.
Classification
The amphoteric surfactants described in this section are not included in Annex 1 of
list of dangerous substances of Council Directive 67/548/EEC.
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