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EC number: 251-995-5 | CAS number: 34396-03-7
- Life Cycle description
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- Endpoint summary
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- Density
- Particle size distribution (Granulometry)
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- Auto flammability
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- Endpoint summary
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- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
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- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
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- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
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- Specific investigations
- Exposure related observations in humans
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- Additional toxicological data

Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Details on test solutions:
- Direct dispersion in water. 500 mg test substance was dispersed in approximately 250 ml of water and subjected to ultrasonication for approximately 30 minutes. Synthetic sewage (16 ml), activated sewage sludge (200 ml) and water were added to a final volume of 500 ml to give a test concentration of 1000 mg/l.
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- A mixed population of activated sewage sludge microorganisms was obtained on 7th April 1998 from the aeration stage of the Severn Trent Water Plc sewage treatment plant at Belper, Derbyshire, UK, which treats predominantly domestic sewage. The activated sewage sludge sample was maintained on continuous aeration in the laboratory at a temperature of 21°C and was used on the day of collection. The pH of the sample was 7.3 and the suspended solids equal to 3.7g/l prior to use.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Post exposure observation period:
- At 30 minute and 3 hour contact times, aliquotes were removed from the conical flask and poured into the measuring vessel (250 ml darkened glass Biological Oxygen Demand (BOD) bottle) and the rate of respiration measured using a Yellow Spring dissolved oxygen meter fiitted with a BOD probe. The contents of the measuring vessel were stirred constantly be magnetic stirrer. The rate of respiration for each flask was measured over the linear portion of the oxygen consumption trace for an approximate 10 minute period.
- Test temperature:
- 21°C
- Nominal and measured concentrations:
- Based on the results from a range finding study, the definitive test was carried out as a limit test at a test concentration of 1000 mg/l.
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 500 ml conical flask
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Laboratory dechlorinated tap water
TEST CONCENTRATIONS
- Spacing factor for test concentrations: limit test at 1000 mg/l, in triplicate - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels: EC50 5.2 mg/l - Validity criteria fulfilled:
- yes
- Conclusions:
- An ASRI 3hr EC50 of >1000 mg/l and NOEC of >= 1000 mg/l were determined in a reliable study conducted according to an appropriate test protocol, and in compliance with GLP.
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- Please refer to the attached justification for grouping of substances provided in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: Source: Safepharm Laboratories 1998
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: Source: Hüls 1993
- Duration:
- 5.8 h
- Dose descriptor:
- EC10
- Effect conc.:
- 1 115 other: µl/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks on result:
- other: (Test 1)
- Duration:
- 5.75 h
- Dose descriptor:
- EC10
- Effect conc.:
- 1 421 other: µl/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks on result:
- other: (Test 2)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1993-09-28 to 1993-10-01
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Principles of method if other than guideline:
- Method: Oxygen consumption test (Huls method)
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A 5 l wide-necked bottle, with magnetic stirrer and 3520 ml distilled aqua, was covered with aluminum foil and autoclaved for 30 minutes at 120°C and 1 bar. After cooling down to room temperature, 200 ml of sterile stock solution and 90 ml seed suspension (liquid culture of the test organism, about 19 hrs incubation, count 10 x 105 cells / ml) were stirred for 5 minutes.
The test substance was pipetted directly into the test bottles. Subsequently, the emulsifier was added. Then the flasks were completely filled with the inoculated culture solution and stoppered.
Emulsifier additive: Nonylphenol ethoxylated propoxylated (EO 10Mol PO 5Mol). - Test organisms (species):
- Pseudomonas putida
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 5.8 h
- Post exposure observation period:
- At the end of the examination, 1 ml HgCl2 solution (final concentration about 3 mg HgCl2/l) was added to each flask to stop the biochemical reactions. Subsequently, the oxygen measurements were performed.
- Test temperature:
- Test 1: 24.7 - 25.0°C. Test 2: 24.8 - 25.1°C
- Nominal and measured concentrations:
- Test 1: 500, 1000, 1500, 2000 µl/L. Test 2: 1000, 1500, 1750, 2000 µl/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type (delete if not applicable): closed
- Material, size, headspace, fill volume: 100mL glass flasks with ground glass stopper
- No. of vessels per concentration (replicates): Four, two with HgCl2
- No. of vessels per blank (replicates): Nine, four with HgCl2
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : oxygen content of the test solutions measured using oxygen electrode. - Reference substance (positive control):
- no
- Duration:
- 5.8 h
- Dose descriptor:
- EC10
- Effect conc.:
- 1 115 other: µl/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: (Test 1)
- Duration:
- 5.75 h
- Dose descriptor:
- EC10
- Effect conc.:
- 1 421 other: µl/l
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: (Test 2)
- Details on results:
- Mean bacteria-inhibiting concentration: 1268µl/l (1.3 ml/l to 2 significant figures)
- Conclusions:
- A 5hr EC10 of 1.3 ml/l for toxicity to Pseudomonas putida was determined in a reliable study conducted according to an appropriate test protocol and in compliance with GLP.
Referenceopen allclose all
Table 1: Controls, reference substance (3, 5-dichlorophenol) and test substance: oxygen consumption and percentage inhibition of the respiration rate.
Flask |
Nominal concentration (mg/l) |
Oxygen consumption rate (mg O2/l/min) |
% Inhibition respiration rate |
Inoculum control |
- |
0.48 |
- |
Inoculum control |
- |
0.40 |
- |
|
|||
Test substance |
1000 |
0.42 |
5 |
Test substance |
1000 |
0.42 |
5 |
Test substance |
1000 |
0.46 |
5 |
|
|||
Reference substance |
32 |
0.05 |
89 |
Reference substance |
10 |
0.11 |
75 |
Reference substance |
3.2 |
0.31 |
30 |
Test 1:
|
|||||
Control |
Test substance concentration: |
||||
500µl/L |
1000µl/L |
1500µl/L |
2000µl/L |
||
Oxygen concentration in flasks with HgCl2at start of incubation |
8.44 |
|
|||
8.28 |
|||||
8.63 |
8.65 |
8.55 |
8.57 |
8.52 |
|
8.43 |
8.54 |
8.32 |
8.47 |
8.43 |
|
Average value |
8.45 |
8.60 |
8.44 |
8.52 |
8.48 |
Oxygen concentration in flasks without HgCl2at end of incubation |
4.07 |
|
|||
4.01 |
|||||
4.04 |
4.03 |
4.36 |
4.62 |
5.14 |
|
4.02 |
4.05 |
4.61 |
4.50 |
5.25 |
|
Average value |
4.04 |
4.04 |
4.49 |
4.56 |
5.20 |
O2Consumption during incubation |
4.41 |
4.56 |
3.95 |
3.96 |
3.28 |
Absolute difference during incubation |
|
-0.14 |
0.46 |
0.45 |
1.13 |
% effect during incubation |
|
-3.3 |
10.4 |
10.2 |
25.6 |
Test 2:
|
|||||
Control |
Test substance concentration: |
||||
1000µl/L |
1500µl/L |
1750µl/L |
2000µl/L |
||
Oxygen concentration in flasks with HgCl2at start of incubation |
8.22 |
|
|||
7.89 |
|||||
8.05 |
8.23 |
8.11 |
8.10 |
8.08 |
|
8.16 |
8.26 |
8.30 |
8.26 |
8.12 |
|
Average value |
8.08 |
8.25 |
8.21 |
8.18 |
8.10 |
Oxygen concentration in flasks without HgCl2at end of incubation |
4.04 |
|
|||
3.89 |
|||||
3.90 |
4.25 |
4.64 |
4.70 |
4.94 |
|
3.99 |
4.27 |
4.69 |
4.50 |
4.73 |
|
Average value |
3.96 |
4.26 |
4.67 |
4.60 |
4.84 |
O2Consumption during incubation |
4.13 |
3.99 |
3.54 |
3.58 |
3.27 |
Absolute difference during incubation |
|
0.14 |
0.59 |
0.55 |
0.86 |
% effect during incubation |
|
3.4 |
14.2 |
13.2 |
20.8 |
Description of key information
3-h NOEC >= 1000 mg/L (OECD 209; read-across from CAS No. 142877-45-0).
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 1 000 mg/L
Additional information
Note: A study on the toxicity towards aquatic microorganisms according to OECD guideline 209 is currently ongoing for the analogue substance (i.e. trichloro(2,4,4 -trimethylpentyl)silane (CAS 18379-25 4)), which shares the same silanol hydrolysis product as the registered compound. This dossier will be updated with a read-across to the above mentioned analogue substance once the final study report is available.
There are no microorganism toxicity data available for trimethoxy(2,4,4-trimethylpentyl)silane (CAS No. 34396-03-7), therefore good quality data for the structurally analogue substances trimethoxy(2-methylpropyl)silane (CAS No. 18395-30-7) and (2,3-Dimethyl-2-butanyl)(trimethoxy)silane (CAS No. 142877-45-0) have been read across.
All substances share related hydrolysis products (2,4,4-trimethylpentyl)silanetriol, (2-methylpropyl)silanetriol and (1,1,2-trimethylpropyl)silanetriol; the other hydrolysis product is methanol. Methanol does not have adverse effects on microorganisms (OECD, 2004). Both substances are expected to undergo minimal hydrolysis within the timescale of an ASRI test.
All substances are within a wider analogue group than the trimethoxy(2,4,4-trimethylpentyl)silane analogue group. Substances within this wider analogue group, in general, exhibit no evidence of significant toxicity to microorganisms. It is therefore considered valid to read-across the results for trimethoxy(2-methylpropyl)silane (CAS No. 18395-30-7) and from (2,3-Dimethyl-2-butanyl)(trimethoxy)silane (CAS No. 142877-45-0) to fill the data gap for the registered substance. This wider analogue group for the toxicity to microorganisms endpoint consists of a number of sub-classes of substances. However, read-across is carried out between substances with the same sub-class in most cases. Table 7.4.2 presents microorganism toxicity data available for substances within the sub-class of alkoxysilanes, silanols, acetoxysilanes and chlorosilanes, etc., where the Si part is of low-biological reactivity, once any hydrolysis is accounted for.
Table 7.4.2 Microorganism toxicity data available for substances within the relevant sub-class of chemicals
CAS |
Name |
Result: E(I)C50 (mg/l) |
Result: NOEC (or EC10/ EC20) (mg/l) |
Guideline Number |
Test method |
Species |
Duration |
Reliability |
001000-50-6 |
Butylchlorodimethylsilane |
>340 |
|
88/302/EC |
ASRI |
|
3h |
1a |
001066-40-6 |
Hydroxytrimethylsilane |
6670 |
|
OECD 209 and ISO 1892 |
ASRI |
|
Uncertain |
1a |
001185-55-3 |
Trimethoxy(methyl)silane |
>100 |
|
OECD 209 |
ASRI |
|
3hr |
1a |
031795-24-1 |
Potassium methylsilanetriolate |
>100 |
|
OECD 209 |
ASRI |
|
3 h |
1a |
087135-01-1 |
1,6-Bis(trimethoxysilyl)hexane |
>1000 |
|
OECD 209 |
ASRI |
|
3h |
1a |
017980-47-1 |
Triethoxyisobutylsilane |
>1000 |
≥1000 |
OECD 209 |
ASRI |
|
3h |
1a |
005894-60-0 |
Trichloro(hexadecyl)silane |
>1000 |
|
OECD 209 |
ASRI |
|
3h |
1a |
016415-12-6 |
Hexadecyltrimethoxysilane |
>1000 |
|
OECD 209 |
ASRI |
|
3 hr |
1a |
002943-75-1 |
Triethoxyoctylsilane |
>1000 |
|
OECD 209 |
ASRI |
|
3 hr |
1a |
016068-37-4 |
4,4,7,7-tetraethoxy-3,8-dioxa-4,7-disiladecane |
>8000 |
8000 |
DIN 38 412, Part 8 (Pseudomonas cell multiplication inhibition test) |
growth inhibition test |
P putida |
16 h |
1c |
035435-21-3 |
Triethoxy(2,4,4-trimethylpentyl)silane |
>100 |
|
OECD 209 |
ASRI |
|
3hr |
1a |
018395-30-7 |
Trimethoxy(2-methylpropyl)silane |
|
EC10 1.3 ml/l |
Huls AG method |
oxygen consumption |
P putida |
5.8 h |
2c -don't use to derive PNEC |
142877-45-0 |
Silane, trimethoxy(1,1,2-trimethylpropyl)- |
>1000 |
≥1000 |
OECD 209 |
ASRI |
|
3 hr |
1a |
013154-25-1 |
Chlorotri(3-methyl-propyl)silane |
>1000 |
100 |
OECD 209 |
ASRI |
|
3 hr |
2b |
126990-35-0 |
Dicyclopentyldimethoxysilane |
>water solubility |
|
OECD 209//EU C11/Huls AG method (WOE) |
ASRI/ASRI/oxygen consumption P putida |
|
3 hr |
1a/1a/2c |
139147-73-2 |
Silane, dichlorodicyclopentyl- |
>100 |
|
OECD 209 |
ASRI |
|
3 hr |
1a |
Additional information is given in a supporting report (PFA, 2013j) attached in Section 13 of the IUCLID dossier.
The influence of the test item on the respiration rate on the activated sludge was investigated in a 3-h limit test test according to the OECD guideline 209 and under GLP conditions (Safepharm, 1998). The concentration of the test item in the limit test was 1000 mg/l. Up to and including the concentration of 1000 mg/l, the test item had no significant inhibitory effect on the respiration rate of activated sludge after the incubation period of three hours. The EC50 was at > 1000 mg/l and the NOEC at ≥ 1000 mg/l. In view of the rapid hydrolysis it is likely that the test organisms were exposed predominantly to the hydrolysis products of the tested substance.
Based on the results with the read-across substance, no toxicity of trimethoxy(2,4,4-trimethylpentyl)silane (CAS No. 34396-03-7) and its silanol hydrolysis product (2,4,4-trimethylpentyl)silanetriol are expected towards activated sludge microorganisms for concentrations relevant for sewage treatment plants.
A second study with Pseudomonas putida was available (Hüls AG, 1993). A 5-hr EC10 of 1.3 ml/l for toxicity to Pseudomonas putida was determined in a reliable study conducted according to an appropriate test protocol and in compliance with GLP.
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