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EC number: 264-709-9 | CAS number: 64157-14-8
- 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 aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 13 - 15 Feb 2019
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- limited significance of analytical dose verification
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes
Test material
- Reference substance name:
- Hydrogen tetrakis[2,2-bis[(allyloxy)methyl]butan-1-olato-O1]bis(ditridecyl phosphito -O'')titanate(2-)
- EC Number:
- 264-709-9
- EC Name:
- Hydrogen tetrakis[2,2-bis[(allyloxy)methyl]butan-1-olato-O1]bis(ditridecyl phosphito -O'')titanate(2-)
- Cas Number:
- 64157-14-8
- Molecular formula:
- not applicable (UVCB substance)
- IUPAC Name:
- dihydrogen 2-{[(di{[bis(tridecyloxy)phosphanyl]oxido}tris({2,2-bis[(prop-2-en-1-yloxy)methyl]butyl}oxido)titaniotetrakis(ylium))oxido]methyl}-1-(prop-2-en-1-yloxy)-2-[(prop-2-en-1-yloxy)methyl]butane
- Test material form:
- liquid
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Remarks:
- LC-MS/MS (for reference substance Trimethylolpropane diallyl ether), ICPMS (for reference substance Titanium )
- Details on sampling:
- - Concentrations (TMPDAE): control, level 1 (nominal loading rate: 0.65 mg/L) , and level 5 (nominal loading rate: 10 mg/L) test solution at initiation (0 hour) and in control and level 1 at termination (48 hours) of the definitive test.
- Concentrations (titanium) : control, level 1 and level 5 test solution samples at initiation (0 hour) of the definitive test. The 0-hour samples were measured in fresh parent test solutions and the 48-hour samples were measured from a composite of the spent.
- Sampling method (TMPDAE): 5-mL sample was collected from the control and levels 1 and 5 test substance treatments for TMPDAE analysis using a serological pipette and placed in separate 10-mL culture tubes.
- Sampling method (titanium): At the 0-hour sampling point, a 5-mL sample was collected from the control and levels 1 and 5 test substance treatments for titanium analysis using a serological pipette, placed in separate 15-mL Falcon™ tubes.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The five test solutions were prepared separately as water accommodated fractions (WAF). Test substance was weighed onto glass cover slips and dropped into glass aspirator bottles containing 2.0-L of dilution water to prepare the test substance solutions. The aspirator bottles were stirred for approximately 22 hours with a vortex <25% of the solution depth. After approximately 22 hours, the solutions were removed from the stir plates and allowed to settle for approximately 1-2 hours. After settling, the level 1 through level 4 (nominal loading rates: 0.65 - 5 mg/L) solutions appeared clear and colorless. The level 5 solution (nominal loading rate: 10 mg/L) appeared clear and colorless with a very light scattered surface film. After the 1-2 hour settling, approximately 100 mL of each solution was discarded, and approximately 1 L of each solution was collected and used to prepare the replicate test treatment chamber solutions.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Source: obtained from an in-house daphnid culture
- Parental stock: Less than 24 hours old neonates for the definitive test were collected from in-house culture containing adults that were approximately 16 days old. The adults were considered acceptable with no signs of stress, disease or physical damage.
- Feeding during test: no
- Holding conditions: All daphnids were cultured in a temperature-controlled area at approximately 20°C. During the culture period, the daphnids were fed a suspension of the algal species Pseudokirchneriella subcapitata at least once a day supplemented by an artificial diet consisting of a wheat grass, salmon starter, and yeast suspension. Less than 24 hours old neonates for the definitive test were collected from in-house culture containing adults that were approximately 16 days old. The adults were considered acceptable with no signs of stress, disease or physical damage.
ACCLIMATION
- Since the culturing and testing environmental parameters were equivalent (i.e., temperature, dilution water, and lighting), no acclimation period was necessary.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 146 mg CaCO3/L
- Test temperature:
- 20.0°C - 20.6°C
- pH:
- 8.5 - 8.7
- Dissolved oxygen:
- 7.6 - 8.6 mg/L
- Conductivity:
- 335 µS/cm
- Nominal and measured concentrations:
- Nominal loading rates: 0 (control), 0.65, 1.3, 2.5, 5.0, and 10 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250-mL glass jars
- Type: closed with a clear plastic Petri dish
- Fill volume: 200 mL
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: The dilution water was a moderately hard freshwater prepared by blending naturally hard well water with well water that was demineralized by reverse osmosis (RO). The well water and RO water were blended together to yield a total hardness of 130 to 160 mg CaCO3/L. Prior to use, the dilution water was passed through a sediment filter.
- Culture medium different from test medium: no
- Intervals of water quality measurement: Total hardness, total alkalinity, and conductivity were measured in the dilution water at test initiation. Temperature, dissolved oxygen concentration, and pH were measured at initiation and termination in all replicates.
OTHER TEST CONDITIONS
- Photoperiod: 16/8 hours light/dark cycle
- Light intensity: 728 lux
EFFECT PARAMETERS MEASURED: Daphnids were observed for immobility and sublethal effects at approximately 24 and 48 hours after test initiation. - Reference substance (positive control):
- no
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- 3.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95%-CI: 2.9 - 4.4 mg/L
- Duration:
- 24 h
- Dose descriptor:
- EL50
- Effect conc.:
- 6.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95%-CI: 6.4 - 7.3 mg/L
- Duration:
- 48 h
- Dose descriptor:
- other: NOEL
- Effect conc.:
- 0.65 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: At 24 hours two daphnids in the 1.3 mg/L and two daphnids in the 5.0 mg/L test substance treatments were noted as floating. At 48 hours five daphnids in the 1.3 mg/L and three daphnids in the 5.0 mg/L test
substance treatments were noted as floating
Any other information on results incl. tables
BIOLOGICAL RESULTS:
Table 1: Immobility and percent unaffected of Daphnia magna exposed to KR®55 for 48 hours under static test conditions
Nominal Test Substance Loading Rate (mg/L) |
Cumulative Immobile (% Immobility) |
48-Hour Mean Percentage Immobility |
48-Hour Mean Percentage Unaffected a |
|||||||
24 Hours |
48 Hours |
|||||||||
A |
B |
C |
D |
A |
B |
C |
D |
|||
0 (Control) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 |
100 |
0.65 |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 |
100 |
1.3 |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
0 |
75 * |
2.5 |
0 (0) |
0 (0) |
0 (0) |
1 (20) |
4 (80) |
5 (100) |
3 (60) |
4 (80) |
80 |
20 * |
5.0 |
0 (0) |
0 (0) |
0 (0) |
0 (0) |
1 (20) |
1 (20) |
1 (20) |
1 (20) |
20 |
65 * |
10 |
5 (100) |
5 (100) |
5 (100) |
5 (100) |
5 (100) |
5 (100) |
5 (100) |
5 (100) |
100 |
0 * |
a Percentage unaffected was percentage of daphnids showing no sublethal observations and no immobility at the end of the definitive test (48 hours), with 100% meaning no affected daphnid and 0% meaning all daphnids showing sublethal observations or immobility.
* Statistically significant decrease in percent unaffected compared to the control (Dunnett’s One-Tailed Test and Fisher’s One- Tailed Exact Test with Hochberg’s familywise adjustment).
Notes: Five daphnids were placed in each replicate at test initiation, totaling 20 daphnids per treatment.
ANLYTICAL RESULTS:
TMPDAE:
Table 2: Measured concentrations of TMPDAE during the 48-hour acute toxicity test with Daphnia magna to KR®55
Nominal KR®55 Test Substance Loading Rate (mg/L) |
Measured TMPDAE Concentrationaas mg/L |
||
0 Hour |
48 Hours |
Mean Measured |
|
0 (control) |
<LOD b |
<LOD b |
<LOD b |
0.65 |
0.139 |
0.133 |
0.136 |
1.3c |
NA |
NA |
NA |
2.5c |
NA |
NA |
NA |
5.0c |
NA |
NA |
NA |
10 |
2.27 |
--e |
NA |
QC Fortification Spikes (% Recovery) |
|||
Low Spike (0.00194) d |
0.00205 (105) 0.00199 (103) 0.00195 (100) |
0.00200 (103) 0.00206 (106) |
NA |
High Spike (121) d |
121 (100) 127 (105) 125 (104) |
121 (100) 127 (105) |
NA |
a Measured Concentration (mg/L) = Measured concentration from curve (ng/mL) × analysis volume (mL) / sample volume (mL) / 1,000 (ng/L / mg/mL).
b LOD = 0.000581 mg/L.
c TMPDAE concentrations measured in lowest and highest treatments only. No samples collected from levels 2, 3, and 4.
d Nominal concentration in mg TMPDAE/L.
e No sample collected due to 100% immobility.
NA = Not applicable.
Titanium:
Table 3: Measured concentrations of titanium at 0 Hour During the 48-Hour acute toxicity test with Daphnia magna to KR®55
Nominal KR®55 Test Substance Loading Rate (mg/L) |
Measured Titanium Concentrationaas mg/L |
0 Hour |
|
0 (control) |
<LODb |
0.65 |
<LODb |
1.3 c |
NA |
2.5 c |
NA |
5.0 c |
NA |
10 |
<LODb |
QC Fortification Spikes (% Recovery) |
|
Low Spike (0.0100)d |
0.00753 (75) |
Mid Spike (0.100) d |
0.0992 (99)e |
High Spike (10.0) d |
10.3 (103)f |
aMeasured Concentration (mg/L) = Measured concentration from curve (mg/L) × analysis volume (mL) / sample volume (mL).
b LOD = 0.00300 mg/L.
cTitanium concentrations measured in lowest and highest treatments only. No samples collected from levels 2, 3, and 4.
d Nominal concentration in mg titanium/L.
e Re-diluted in duplicate and re-analyzed, mean of duplicate re-analyses reported.
f Re-diluted in duplicate and re-analyzed, mean of original and duplicate re-analyses reported.
NA = Not applicable.
VALIDITY CRITERIA:
Table 4: Validity criteria for OECD 202.
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
In the control, including the control containing the solubilising agent, not more than 10% of the daphnids should have been immobilized. |
Immobilization among control daphnids was |
yes |
The dissolved oxygen concentration at the end of the test should be ≥ 3 mg/L in control and test vessels. |
The dissolved oxygen concentration at the end of the test was ≥ 8.3 mg/L in control |
yes |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to “Any other information on results incl. tables”.
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