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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:
05 April 2018 - 13 June 2018
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2018

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
Version / remarks:
1992
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
Version / remarks:
2008
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

1
Chemical structure
Reference substance name:
4,4'-Isopropylidenediphenol, oligomeric reaction products with 1-chloro-2,3-epoxypropane, reaction products with trimethylhexane-1,6-diamine
EC Number:
500-332-0
EC Name:
4,4'-Isopropylidenediphenol, oligomeric reaction products with 1-chloro-2,3-epoxypropane, reaction products with trimethylhexane-1,6-diamine
Cas Number:
153195-44-9
Molecular formula:
(C15 H16 O2 . C9 H22 N2 . C3 H5 Cl O)x
IUPAC Name:
4,4'-Isopropylidenediphenol, oligomeric reaction products with 1-chloro-2,3-epoxypropane, reaction products with trimethylhexane-1,6-diamine
Test material form:
liquid

Study design

Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic, non-adapted
Details on inoculum:
- Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): A mixed population of sewage treatment micro-organisms was obtained on 14 May 2018 from the final effluent stage of the Severn Trent Water Plc sewage treatment plant at Loughborough, Leicestershire, UK, which treats predominantly domestic sewage.
- Preparation of inoculum for exposure: The sample of effluent was filtered through coarse filter paper (first approximate 200 mL discarded) and maintained on aeration in a temperature controlled room at temperatures of between 20 and 22 ºC prior to use.
Duration of test (contact time):
28 d
Initial test substance concentration
Initial conc.:
20 mg/L
Based on:
test mat.
Parameter followed for biodegradation estimation
Parameter followed for biodegradation estimation:
O2 consumption
Details on study design:
TEST CONDITIONS
- Composition of medium: mineral medium as recommended in the OECD Guidelines
- Solubilising agent (type and concentration if used): acetone
A nominal amount of test item (1000 mg) was dissolved in 10 mL of acetone to give a 1000 mg/10 mL solvent stock solution. An aliquot (500 µL) of this solvent stock solution was dispensed onto a filter paper and the solvent allowed to evaporate to dryness for approximately 15 minutes. The filter paper was dispersed in approximately 350 mL of mineral medium with the aid of high shear mixing (approximately 7500 rpm, 5 minutes) prior to addition of inoculum. The volume was then adjusted to 500 mL to give a final concentration of 100 mg/L. The volumetric flask containing the solvent stock solution was inverted several times to ensure homogeneity of the solution.
- Test temperature: 20 - 22 ºC
- pH: 7.6 at test start
- pH adjusted: no
- Continuous darkness: diffuse light


TEST SYSTEM
- Culturing apparatus: CES Multi-Channel Aerobic Respirometer
- Number of culture flasks/concentration: 3

SAMPLING
- Sampling frequency: daily

CONTROL AND BLANK SYSTEM
Three replicate bottles containing inoculated mineral medium to act as the inoculum control plus a filter paper.
Two replicate bottles containing inoculated mineral medium plus a filter paper and the reference item, aniline, at a concentration of 100 mg/L.
Two replicate bottles containing the test item on filter paper at a concentration of 20 mg/L in inoculated mineral medium plus the reference item, aniline, at a concentration of 100 mg/L to act as toxicity control vessels.

Reference substance
Reference substance:
aniline

Results and discussion

% Degradationopen allclose all
Parameter:
% degradation (O2 consumption)
Value:
0
Sampling time:
28 d
Parameter:
% degradation (O2 consumption)
Remarks:
toxicity control
Value:
41
Sampling time:
14 d
Details on results:
The mean BOD of the inoculated mineral medium (control) was 14.91 mg O2/L after 28 days and therefore satisfied the validation criterion given in the OECD Test Guidelines.
The pH of the inoculated test item vessels on Day 28 were 7.6 and hence satisfied the validation criterion given in the OECD Test Guidelines.
The difference between extremes of replicate BOD values at the end of the test was less than 20% and therefore satisfied the validation criterion given in the OECD Test Guidelines.
The test item attained 0% biodegradation after 28 days, calculated from the oxygen consumption values, and therefore cannot be considered to be readily biodegradable under the strict terms and conditions of OECD Guideline No. 301F.
The toxicity control attained 41% biodegradation after 14 days and 45% biodegradation after 28 days.
There was a statistically significant difference (P≥0.05) between the inoculum control and test item Day 28 BOD values. The test item was therefore considered to have had an adverse effect on the sewage treatment micro-organisms used in the test.
Therefore, care should be taken in the interpretation of these results as the test item was considered to have exhibited an inhibitory effect at the test concentration employed in the study as significant differences were shown between the Day 28 inoculum control and test item BOD values.

BOD5 / COD results

Results with reference substance:
Aniline (procedure control) attained 62% biodegradation after 14 days and 71% biodegradation after 28 days thereby confirming the suitability of the inoculum and test conditions.

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Interpretation of results:
under test conditions no biodegradation observed
Conclusions:
The test item attained 0% biodegradation after 28 days and therefore cannot be considered as readily biodegradable under the strict terms and conditions of OECD Guideline No. 301F.
There was a statistically significant difference (P≥0.05) between the inoculum control and test item Day 28 BOD values. The test item was therefore considered to have had an adverse effect on the sewage treatment micro-organisms used in the test.
Therefore, care should be taken in the interpretation of these results as the test item was considered to have exhibited an inhibitory effect at the test concentration employed in the study as significant differences were shown between the Day 28 inoculum control and test item BOD values.
Executive summary:

The study was performed to assess the ready biodegradability of BADGE-TMD adduct in an aerobic aqueous media. The method followed was designed to be compatible with the OECD Guidelines for Testing of Chemicals (1992) No. 301F, “Ready Biodegradability; Manometric Respirometry Test” referenced as method C.4-D of Commission Regulation (EC) No. 440/2008 and US EPA Fate, Transport, and Transformation Test Guidelines OCSPP 835.3110 (Paragraph (q)).

 

In an initial test conducted at a concentration of 100 mg/L, the procedure control failed to attain 60% biodegradation or greater after 14 days and as such did not meet the validation criteria. This study was therefore terminated after 15 days.

In a further test the toxicity control vessel, containing both the test item and aniline, attained less than 25% biodegradation after 14 days. This result indicated that, under the strict terms and conditions of the OECD Guidelines, the test item would be classed as exhibiting inhibitory effects.

Therefore, following the recommendations of the Test Guidelines, in the definitive test the test item at a reduced concentration of 20 mg/L was exposed to sewage treatment micro-organisms with mineral medium in sealed culture vessels in diffuse light at approximately 20 ºC for 28 days.

Following the recommendations of the International Standards Organisation (ISO 1995), the test item was dissolved in an auxiliary solvent prior to being adsorbed onto a filter paper and subsequent dispersal in test media. Using this method, the test item is evenly distributed throughout the test medium and the surface area of test item exposed to the test organisms is increased thereby increasing the potential for biodegradation.

The biodegradation of the test item was assessed by the measurement of daily oxygen consumption values on Days 0 to 28. Control solutions with inoculum and the reference item, aniline, together with a toxicity control were used for validation purposes.

The test item attained 0% biodegradation after 28 days and therefore cannot be considered to be readily biodegradable under the strict terms and conditions of OECD Guideline No. 301F.

The toxicity control attained 41% biodegradation after 14 days and 45% biodegradation after 28 days.

There was a statistically significant difference (P≥0.05) between the inoculum control and test item Day 28 Biological Oxygen Demand (BOD) values. The test item was therefore considered to have had an adverse effect on the sewage treatment micro-organisms used in the test.

Therefore, care should be taken in the interpretation of these results as the test item was considered to have exhibited an inhibitory effect at the test concentration employed in the study as significant differences were shown between the Day 28 inoculum control and test item BOD values.