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Diss Factsheets

Environmental fate & pathways

Biodegradation in water: screening tests

Administrative data

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Study period:
March - May 2008
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Guideline study with GLP.
Cross-referenceopen allclose all
Reason / purpose for cross-reference:
reference to same study
Reason / purpose for cross-reference:
reference to other study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2008
Report date:
2008

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
Deviations:
no
GLP compliance:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
3-[(2-aminoethyl)amino]propane-1-sulfonic acid
Cas Number:
14235-54-2
Molecular formula:
C5H14N2O3S
IUPAC Name:
3-[(2-aminoethyl)amino]propane-1-sulfonic acid
Details on test material:
- Name of test material: "3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" (EPS)
- Physical state: liquid
- Composition of test material, percentage of components: 48.5 % w/w 3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE 51.5 % water
- Lot/batch No.: 06060423/101
- Stability under test conditions: not applicable
- Storage condition of test material: room temperature in the dark
Specific details on test material used for the study:
Details on properties of test surrogate or analogue material (migrated information):
none.

Study design

Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic, non-adapted
Details on inoculum:
- Source of inoculum/activated sludge: sewage treatment works A-2500 Baden, which waste-water catchment is predominantly domestic
- Laboratory culture: On arrival in the laboratory and after sedimentation the clear supernatant was decanted and the sludge was filled up with tap water to its origin volume of 6 L to reduce the carbon content. The sample was aerated by means of a filtered compressed air before being used for the study.
- Pretreatment: none.
- Concentration of sludge: The concentration of the final suspended solids of the sludge in all vessels was nominally ca. 20 mg/L.
Duration of test (contact time):
28 d
Initial test substance concentrationopen allclose all
Initial conc.:
93.9 mg/L
Based on:
test mat.
Initial conc.:
15 mg/L
Based on:
other: carbon
Parameter followed for biodegradation estimation
Parameter followed for biodegradation estimation:
CO2 evolution
Details on study design:
TEST CONDITIONS
- Composition of medium: mineral medium as in the guideline.
- Additional substrate: none.
- Solubilising agent (type and concentration if used): none.
- Test temperature: 22 +- 2 °C.
- pH: determined.
- pH adjusted: no
- Suspended solids concentration: 20 mg/L.
- Continuous darkness: yes.

TEST SYSTEM
- Culturing apparatus: 5 L flasks.
- Number of culture flasks/concentration: 2 negative control flasks, 2 test substance flasks, 1 positive control flask, 1 toxicity control flask.
- Method used to create aerobic conditions: Apparatus for carbon dioxide scrubbing and a mixture of CO2-free oxygen and CO2-free nitrogen, from gas cylinders, in the correct proportions (20 % O2: 80 % N2) were used.
- Test performed in closed vessels.

SAMPLING
- Sampling frequency: The CO2 evolution was determined on Days 1, 2, 4, 6, 8, 10, 14, 19, 24 and 28/29.
Day 0 was the day of the addition of the test substance to the medium.

CONTROL AND BLANK SYSTEM
- Inoculum blank: yes
- Abiotic sterile control: no
- Toxicity control: yes, containing test substance and positive reference substance.
- Other: Positive reference substance.

STATISTICAL METHODS: no.
Reference substance
Reference substance:
benzoic acid, sodium salt

Results and discussion

Preliminary study:
None.
Test performance:
No unusual observations were made.
% Degradation
Parameter:
% degradation (CO2 evolution)
Value:
19
Sampling time:
28 d
Remarks on result:
other: test substance

BOD5 / COD results

Results with reference substance:
Positive control: 70.4 % biodegradation after 6 days. The plateau of biodegradation was reached on about Day 10 and the degradation of the positive reference substance sodium benzoate exceeded the pass level of 60 % on about Day 5. The test is considered to be valid.
Toxicity control: 48.0 % biodegradation after 28 days. Degradation in the toxicity control, which contained sodium benzoate and the test substance, was not indicative of an inhibition of the microbial activity by the test substance.

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Interpretation of results:
other: "3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" cannot be classified as readily biodegradable
Conclusions:
The biodegradability of "3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" was analysed by the determination of carbon dioxide evolution at frequent intervals over a 28 day period.
The method used was that described in Part C.4-C of the EC Commission Directive 92/69/EEC and in the OECD Guideline 301B.

Results
• The reference substance sodium benzoate was degraded by 87.6 % within 10 days.
• Degradation in the toxicity control, which contained sodium benzoate and the test substance, was not indicative of an inhibition of the microbial activity by the test substance.
• The carbon dioxide evolution from "3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" with a nominal concentration of 15 mg carbon/L reached 19.0 % after 28 days of incubation at mean temperatures of
22.5 °C.

Classification
According to the results of this study,"3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" cannot be classified as readily biodegradable.
Executive summary:

The biodegradability of "3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" was analysed by the determination of carbon dioxide evolution at frequent intervals over a 28 day period. The method used was that described in Part C.4-C of the EC Commission Directive 92/69/EEC and in the OECD Guideline 301B.

 

Results

·     The reference substance sodium benzoate was degraded by 87.6 % within 10 days.

·     Degradation in the toxicity control, which contained sodium benzoate and the test substance, was not indicative of an inhibition of the microbial activity by the test substance.

·     The carbon dioxide evolution from "3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" with a nominal concentration of 15 mg carbon/L reached 19.0 % after 28 days of incubation at mean temperatures of 22.5 °C.

Classification

According to the results of this study, "3-[(2-AMINOETHYL)AMMONIO]PROPANE-1-SULFONATE" cannot be classified as readily biodegradable.