Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Ecotoxicological information

Toxicity to microorganisms

Currently viewing:

Administrative data

Link to relevant study record(s)

Reference
Endpoint:
activated sludge respiration inhibition testing
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2005-06-13 to 2005-07-13
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
Version / remarks:
1988
Qualifier:
according to guideline
Guideline:
OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
Version / remarks:
1984
GLP compliance:
yes (incl. QA statement)
Analytical monitoring:
no
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Due to the low solubility of the test item in test water, adequate amounts of the test item were directly weighed into each test flask.
Test organisms (species):
activated sludge, domestic
Details on inoculum:
- Method of cultivation: The sludge was washed by centrifugation and the supernatant liquid phase was decanted. The solid material was resuspended in tap water and again centrifuged. The latter procedure was repeated twice. An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge (g) to its dry weight (g) determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 3 g dry material per litre, were made up with tap water. To this mixture, 50 mL synthetic sewage feed per litre was added, starting two days prior use of the activated sludge. The activated sludge was kept at room temperature under continuous aeration until use. The pH of the activated sludge was 7.3, therefore no adjustment was necessary.
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
3 h
Test temperature:
21 - 22°C
pH:
7.2 at test start
8.0 - 8.2 at test end
Dissolved oxygen:
7.8 - 8.1 mg/L at test start
7.4 - 7.9 mg/L at test end
Nominal and measured concentrations:
Nominal: 10, 32, 100, 320 and 1000 mg/L
Details on test conditions:
TEST SYSTEM
- Test vessel: glass flasks of approximately 1 litre volume and Karlsruher flasks of 250 mL volume
- Aeration: with compressed air (approximately 0.613 litre per minute)
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 2
- Sludge concentration (weight of dry solids per volume): 3 g/L
Reference substance (positive control):
yes
Remarks:
3,5-Dichlorophenol
Key result
Duration:
3 h
Dose descriptor:
EC50
Effect conc.:
> 1 000 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: inhibition of respiration rate
Duration:
3 h
Dose descriptor:
other: EC20
Effect conc.:
> 1 000 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: inhibition of respiration rate
Results with reference substance (positive control):
- Results with reference substance valid? yes
- The following nominal concentrations of the positive control 3,5-Dichlorophenol were tested on the same activated sludge and under identical conditions as the test item: 3,2, 10, and 32 mg/L. In comparison to the controls the respiration rate of the activated sludge was inhibited by 24.3 % at the lowest nominal concentration of 3.2 mg/L. At the nominal concentrations of 10 and 32 mg test item/L, the respiration rate was inhibited by 51.4 and 81.1%, respectively.

Table 1: Influence of the test item and the reference item (3,5 -Dichlorophenol, DCP) on oxygen consumption of activated sludge

Flask No. Treatment Concentration Oxygene consumption
Inhibition pH- values Oxygene concentration
[mg O2/L]
    [mg/L] [mg O2/L_min] % start end start end
1 Control --- 0.350 --- 7.2 8.2 8.1 7.9
10 Control --- 0.390 --- 7.2 8.0 8.0 7.0
    mean 0.370          
  replicate deviation 10.3          
                 
2 3,5-DCP 32 0.070 81.1 7.3 8.2 8.1 8.4
3 3,5-DCP 10 0.180 51.4 7.2 8.2 8.1 8.1
4 3,5-DCP 3.2 0.280 24.3 7.2 8.1 8.2 7.6
                 
5 Y-14877 1000 0.340 8.1 7.2 8.0 7.8 7.6
6 Y-14877 320 0.370 0 7.2 8.0 7.9 7.4
7 Y-14877 100 0.380 -2.7 7.2 8.0 8.0 7.4
8 Y-14877 32 0.360 2.7 7.2 8.1 7.9 7.8
9 Y-14877 10 0.370 0 7.2 8.0 8.0 7.4
Validity criteria fulfilled:
yes
Conclusions:
Based on measured inhibition rates, the 3-hour EC20 and EC50 could not be quantified because up to the highest nominal test concentration of 1000 mg/L less than 20 % inhibition was noted after three hours incubation. Nevertheless, the 3-hour EC20 and EC50 are clearly higher than 1000 mg/L under the present test conditions.

Description of key information

Based on the results of a respiration inhibition test, the 3-hour EC20 and EC50 of 3-ethylheptamethyltrisiloxane are concluded to exceed 1000 mg/L.

Key value for chemical safety assessment

EC50 for microorganisms:
1 000 mg/L

Additional information