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EC number: 217-164-6 | CAS number: 1760-24-3
- 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

Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1994-09-26 to 1994-09-30
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.1 (Acute Toxicity for Fish)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- Samples of test medium were taken at the start of the test and then after 24 hours in the old medium prior to renewal. Samples of freshly prepared medium were taken again when the tst medium was renewed after 24, 48 and 72 hours.
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: A 1000 mg/l stock solution was prepared by mixing for 18 h followed by filtration. The other treatments were prepared by dilution of the stock solution. - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Zebrafish
- Source: West aquarium, Bad Lauterberg, Germany
- Length at study initiation (length definition, mean, range and SD): 3.0 cm +/-0.5 cm
- Feeding during test: none
ACCLIMATION
- Acclimation period: at least 14 days
- Acclimation conditions (same as test or not): yes
- Type and amount of food: TetraMin® at 1% of body weight
- Feeding frequency: Daily
- Health during acclimation (any mortality observed): The fish exhibit normal behaviour and are free from visible signs of disease at the start of the t
est. Mortalities in the 7 days pruior to the test were ≤5% - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Hardness:
- 11.3 ºdH
- Test temperature:
- 20 - 21ºC
- pH:
- 7.7 - 9.6
- Dissolved oxygen:
- 83 - 103% ASV
- Nominal and measured concentrations:
- Nominal concentrations: 0 (Control), 110, 190, 330, 580 and 1000 mg/l
Mean measured concentrations over test: 0 (Control), 116, 194, 344, 676 and 1130 mg/l
The results are interpreted with reference to mean measured concentrations. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 20 litre aquarium
- Type (delete if not applicable): open
- Aeration: Yes, continuous
- Renewal rate of test solution: daily
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Potable water from Gelsenwasser AG
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: 16 hours light, 8 hours dark
EFFECT PARAMETERS MEASURED: Daily mortalities
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.7 - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 597 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Remarks:
- but exposure is to hydrolysis products
- Basis for effect:
- mortality (fish)
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 344 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Remarks:
- but exposure is to hydrolysis products
- Basis for effect:
- mortality (fish)
- Details on results:
- - Mortality of control: 0
- Reported statistics and error estimates:
- The LC50 was determined by graphical interpolation. The NOEC was obtained directly from the raw data.
- Sublethal observations / clinical signs:
Table 1. Test results
Nominal concentration (mg/l)
Mean measured concentration (mg/l)
Percentage mortality after 24 hours
Percentage mortality after 48 hours
Percentage mortality after 72 hours
Percentage mortality after 96 hours
0 (Control)
-
0
0
0
0
110
116
0
0
0
0
190
194
0
0
0
0
330
344
0
0
10
10
580
676
0
0
10
60
1000
1130
10
90
100
100
- Validity criteria fulfilled:
- yes
- Conclusions:
- A 96-h LC50 value of 597 mg/l and NOEC of 344 mg/l have been determined for the effects of the test substance on mortality of Brachydanio rerio. It is likely that the test organisms were exposed to the hydrolysis products of the substance (methanol and N-(3-(trihydroxysilyl)propyl)ethylenediamine).
Reference
Description of key information
96-hour LC50 597 mg/l (measured) (EU C.1), Danio rerio. The LC50 is equivalent to 484 mg/l when expressed in terms of the silanol hydrolysis product, N-(3-(trihydroxysilyl)propyl)ethylenediamine.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 484 mg/L
Additional information
A 96-hour LC50 value of 597 mg/l (measured) has been determined for the effects of the registration substance, N-(3-(trimethoxysilyl)propyl)ethylenediamine (CAS 1760-24-3, EC 217-164-6), on mortality of Danio rerio (Hüls, 1994). The results are expressed relative to geometric mean measured DOC concentrations of the test substance. The test was conducted according to EU Method C.1 and in compliance with GLP. In view of the test media preparation method and exposure regime, it is likely that the test organisms were exposed predominantly to the hydrolysis products of the tested substance (methanol and N-(3-(trihydroxysilyl)propyl)ethylenediamine).
The results may be expressed in terms of concentration of the silanol hydrolysis product, N-(3-(trihydroxysilyl)propyl)ethylenediamine, by applying a molecular weight correction: (MW of silanol = 180.28 / MW of parent = 222.36) * 597 = 484 mg/l.
The pH rose above 9 at the higher concentrations in this study. It is therefore not possible to tell whether the toxicity observed is due to the test substance or the pH. In addition, toxicity due to the amine increases with increasing pH. This is because the unionised form of the amine is the most toxic compared to the ionised form, and the fraction of the unionised form increases at higher pH.
Two other results are available indicating LC50 values in the range 200 to 213 ppm, however the results of these studies are of unassignable reliability.
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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