Environmental and Health Assessment of Substances in Household Detergents and Cosmetic Detergent Products 6. Amphoteric surfactants
6.1 BetainesBetaines 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. 6.1.1 Environmental fateAerobic 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
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. 6.1.2 Effects on the aquatic environmentThe 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
|
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.