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Environmental fate & pathways

Biodegradation in water: screening tests

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Endpoint:
biodegradation in water: inherent biodegradability
Type of information:
(Q)SAR
Adequacy of study:
supporting study
Study period:
08/2017
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
Justification for type of information:
1. SOFTWARE:
- EPI Suite

2. MODEL (incl. version number):
- BIOWIN (v4.10)

3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
- Smiles: O=C(N(C)C)NC1CC(C)(C)CC(CNC(=O)(N(C)C))(C)C1
- Formular: C16 H32 N4 O2
- Mol WT: 312.46
- Strukture: see ch 1.1 "Identification"

4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
[Explain how the model fulfils the OECD principles for (Q)SAR model validation. Consider attaching the QMRF or providing a link]
- Defined endpoint: Biodegradability
- Unambiguous algorithm:
- Biowin1 (Linear Model Prediction)
- Biowin2 (Non-Linear Model Prediction)
- Biowin3 (Ultimate Biodegradation Timeframe)
- Biowin4 (Primary Biodegradation Timeframe)
- Biowin5 (MITI Linear Model Prediction)
- Biowin6 (MITI Non-Linear Model Prediction)
- Biowin7 (Anaerobic Model Prediction)
- Defined domain of applicability: na
- Appropriate measures of goodness-of-fit and robustness and predictivity: na
- Mechanistic interpretation: na

5. APPLICABILITY DOMAIN
[Explain how the substance falls within the applicability domain of the model]
- Descriptor domain: na
- Structural and mechanistic domains:
- Carbon with 4 single bonds and no hydrogens
- Molecular weight parameter (Biowin 1 - 6)
- Methyl [-CH3] (Biowin 5 - 7)
-CH2- [linear] (Biowin 5 - 7)
-CH2- [cyclic] (Biowin 5 - 7)
-CH- [cyclic] (Biowin 5 - 7)
- Equation Constant (Biowin 1 - 6)
- Similarity with analogues in the training set: na
- Other considerations (as appropriate): na

6. ADEQUACY OF THE RESULT
[Explain how the prediction fits the purpose of classification and labelling and/or risk assessment]
Qualifier:
no guideline required
Principles of method if other than guideline:
QSAR
GLP compliance:
not specified
Key result
Parameter:
probability of ready biodegradability (QSAR/QSPR)
Value:
< 0.5
Remarks on result:
not readily biodegradable based on QSAR/QSPR prediction
Remarks:
Biowin 1 - 7

Biowin1 (Linear Model Prediction)   : Does Not Biodegrade Fast

Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast

Biowin3 (Ultimate Biodegradation Timeframe): Months

Biowin4 (Primary Biodegradation Timeframe): Weeks

Biowin5 (MITI Linear Model Prediction)   : Does Not Biodegrade Fast

Biowin6 (MITI Non-Linear Model Prediction): Does Not Biodegrade Fast

Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast

Ready Biodegradability Prediction: NO

 

Conclusions:
Based on QSAR prediction, IPDI-Uron does not biodegrade fast.
Executive summary:

Based on QSAR prediction, IPDI-Uron does not biodegrade fast.

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Study period:
03/2017 - 06/2017
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
Version / remarks:
The higher NaOH concentration is based on years of experience and ensures that the carbon dioxide produced is actually absorbed to the sodium hydroxide completely (see deviations from guideline).
Deviations:
yes
Remarks:
NaOH concentration used for CO2-Absorption in the gas wash bottles is higher (0.2 M) than indicated in the guidelline (0.05 M).
GLP compliance:
yes (incl. QA statement)
Specific details on test material used for the study:
Batch: 703709
Purity: 100 %
CoA: 2017-02-15
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic (adaptation not specified)
Details on inoculum:
Activated sludge from the municipal wastewater treatment plant Breisgauer Bucht was used as
inoculum with a concentration corresponding to 30 mg dry solids per litre. The treatment plant
clarifies predominantly domestic wastewater and has a capacity of 600.000 inhabitant
equivalents. Sampling date of activated sludge was on 03 April 2017. The dry solid content of the
activated sludge was 5.09 g/L. It was determined by weight measurements after drying at 105°C
for 4 hours (mean of triplicate measurements). The activated sludge was washed twice with tap
water by settling the sludge, decanting the supernatant and re-suspending the sludge.
Duration of test (contact time):
ca. 28 d
Initial conc.:
>= 19.8 - <= 19.9 mg/L
Based on:
TOC
Initial conc.:
>= 48.2 - <= 48.5 mg/L
Based on:
test mat.
Parameter followed for biodegradation estimation:
inorg. C analysis
Reference substance:
benzoic acid, sodium salt
Key result
Parameter:
% degradation (CO2 evolution)
Value:
ca. 0.3
Sampling time:
28 d
Validity criteria fulfilled:
yes
Interpretation of results:
not readily biodegradable
Conclusions:
The test item did not reach the criteria for ready biodegradability (60% of ThCO2 within a 10-d window).
Executive summary:

No degradation of the test item could be measured during the test duration. The mean

degradation extent at the end of the test was -0.3%.

The degradation extent in the toxicity control was 47.8% within 14 days, the test substance had

no inhibitory effect on the inoculum.

The reference compound sodium benzoate reached the pass levels for ready biodegradability

within 4 days.

The mean CO2-evolution of the blank flasks was 32.0 mg/L on day 28 after acidification.

Description of key information

Ready biodegradability was assessed by modified Sturm test (OECD 301B, CO2 evolution test) and calculated by QSAR (EPI Suite, Biowin 4.10).

Key value for chemical safety assessment

Biodegradation in water:
not biodegradable

Additional information

QSAR calculation showed that the test item will not degrade fast.