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EC number: 203-492-7 | CAS number: 107-46-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- 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
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- 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
- Study period:
- 2001-02-15 to 2001-03-07
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to an appropriate OECD test guideline, and in compliance with GLP.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Tertiary butyl alcohol was used as a solvent in the five lower test solutions. HMDS was dosed directly in the 2 highest concentrations. - Test organisms (species):
- activated sludge, domestic
- Details on inoculum:
- Activated sludge from a domestic sewage oxidation ditch situated at the district of Hazerswoude Dorp, The Netherlands, taken on 5th March 2001.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Post exposure observation period:
- The oxygen concentration was recorded every minute during a period of about 10 minutes.
- Test temperature:
- 20 ± 2 °C
- pH:
- 8.1 to 8.3
- Nominal and measured concentrations:
- Nominal concentrations were 0, 0.10, 0.32, 1.0, 3.2, 11, 39 and 100 mg/l.
- Details on test conditions:
- TEST SYSTEM
- Test vessel: One litre glass beaker and BOD bottle
- Aeration: All suspensions were aerated vigorously.
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Dilution water prepared by adding 1 ml of stock 1 to 4 to each litre of ultrapure water and store at 20 deg C in the dark with aeration. Prescription according to NEN 6634 [3].
- Vehicle: Tertiary butyl alcohol (TBA)
- Particulate matter: Activated sludge = 4.0 g (dw)/l
- Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 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:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- The two controls had a difference in respiration rate of 2.6%, less than the 15% limit for a valid study. The validity criteria of the Guideline were fulfilled.
- Results with reference substance (positive control):
- A positive control test with 3,5-dichlorophenol yielded an EC50 of 13.1 mg/l. The validity criteria of the Guideline were fulfilled.
- Validity criteria fulfilled:
- yes
- Conclusions:
- A NOEC of >=100mg/l and EC50 >100 mg/l for toxicity to microorganisms were determined in a reliable study conducted according to an appropriate test protocol, and in compliance with GLP.
Reference
No inhibition of the respiration rate was observed within the entire concentration range. Based on nominal test concentrations, the NOEC of HMDS was >= 100 mg/l. The EC50 was >100 mg/l.
Table 1: Results of the activated sludge respiration inhibition test
Test sample |
Nominal concentration of test substance (mg/l) |
Respiration rate (mg O2/g/h) |
Coefficient of determination |
% Inhibition respiration rate |
pH |
Hexamethyldisiloxane |
|
|
|||
Initial control |
0 |
18.6 |
-1.0000 |
-1.3 |
8.2 |
Final control |
0 |
18.1 |
-0.9999 |
1.3 |
8.2 |
0.1 |
19.8 |
-1.0000 |
-0.8 |
8.2 |
|
0.32 |
20.0 |
-1.0000 |
-9.1 |
8.2 |
|
1 |
19.5 |
-1.0000 |
-6.4 |
8.1 |
|
3.2 |
19.6 |
-1.0000 |
-6.9 |
8.1 |
|
11 |
20.6 |
-1.0000 |
-12.0 |
8.1 |
|
39 |
21.0 |
-1.0000 |
-14.1 |
8.1 |
|
100 |
20.7 |
-1.0000 |
-12.9 |
8.1 |
|
|
|
||||
3,5-dichlorophenol |
|
|
|||
Initial control |
0 |
15.7 |
-0.9999 |
7.0 |
8.2 |
Final control |
0 |
18.1 |
-0.9999 |
-7.0 |
8.2 |
5 |
14.6 |
-0.9998 |
13.7 |
8.3 |
|
12 |
8.9 |
-1.0000 |
47.7 |
8.3 |
|
30 |
3.5 |
-0.9743 |
79.4 |
8.3 |
Description of key information
Toxicity to microorganisms: 3hr ASRI NOEC >=100mg/l; EC50 >100 mg/l (OECD 209)
Key value for chemical safety assessment
Additional information
Three reliable studies are available for toxicity to microorganisms.
Two reliable studies are ASRI (activated sludge respiration inhibition) studies. The key study (Mayer 2001) was chosen as the most recent study. This study gave a result of NOEC (3 h) ≥100 mg/l; EC50>100 mg/l. The result from the other reliable ASRI study (Diefenbach 1998) was EC50(3 h) >2000 mg/l.
A reliable study for growth inhibition for Pseudomonas putida is also available (Hanstveit 1999). The result was EC50(17 h) >100 mg/l.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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