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EC number: 923-927-0 | CAS number: -
- 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
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 48 hours
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Batch/Lot No. 115829/70
Appearance Clear, particulate free liquid
Purity (wt.%) 54.7
Storage conditions Room temperature (in sealed container)
Expiry date December, 2019
- Analytical monitoring:
- yes
- Details on test solutions:
- M4 medium was used as culturing and dilution water, and was prepared according to the method of OECD Guideline (2004). This test item was fully soluble in dilution water.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The ephippia was obtained from MicroBioTests Inc. Belgium (imported date: January 16, 2018). Daphnia has been cultured successively for a generation in invertebrate culture room, Environmental Toxicology Research Center, Gyeongnam Department of Environmental Toxicology and Chemistry, Korea Institute of Toxicology (KIT).
Brood stock of Daphnia magna were cultured under 16 h light: 8 h dark with 30 min transition period at 18-22 ºC in glass beakers containing three liters of M4 medium. Cultures were fed daily with a suspension of Pseudokirchneriella subcapitata and the amount (3 mL/L vessel/day) of the supplied algae was range of 6 x 106-107 cell/mL. 1 mL/L of YCT (Yeast, Chlorophyll and Tetramine, NeoEnbiz, Korea) was feed twice in a week. Culture conditions ensured that reproduction was by parthenogenesis.
Gravid adults were isolated 24 hours prior to initiation of the test. Young daphnids produced overnight (< 24 hours old) were used for testing. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 254 mg/L
- Test temperature:
- 19.5-20.4 ºC
- pH:
- 4.57-8.64
- Dissolved oxygen:
- 7.67-8.95mg/L
- Nominal and measured concentrations:
- The measured concentrations were 7.85, 14.6, 26.6, 50.8 and 91.9 mg/L (81.8-91.9% of nominal concentration) for nominal concentrations of 9.6, 17.2, 30.9, 55.6 and 100 mg/L at 0 hour.
- Details on test conditions:
- TEST SYSTEM
Crystallizing dish containing 100 mL of test solution for each replicate was used for toxicity test.
20 daphnids, divided into four groups of five daphnids each, were used for each test concentration and control groups (dilution water).
OTHER TEST CONDITIONS
- Photoperiod: 16 hours of light and 8 hours of dark, including 30-minute dawn and dusk transition periods
- Light intensity: 1161-1268 lux.
RANGE-FINDING STUDY
The range-finding test was conducted at the nominal concentrations of 0.1, 1, 10 and 100 mg/L
by static system. 5 daphnids were exposed in each test vessel and immobilization was observed
during 48 hours. Based on the result of the range-finding test, no immobilization was observed in 0.1-10 mg/L
and 100% immobilization was observed in 100 mg/L of test solution.
Water quality parameters of pH, dissolved oxygen and temperature were measured in each surviving test vessel at 0 and 48 hours of the test.
Daphnia were examined daily for symptoms of intoxication and immobilization. The animals were considered to be immobilized if they were unable to swim for approximately 15 seconds after gentle agitation. - Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 68.9 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 51.6 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- No remarkable phenomenon was observed in all test solutions throughout test period. There was no immobilization and symptoms of intoxication observed in control groups and 9.6, 17.2, 30.9, 55.6 mg/L of test solutions (mean measured concentrations: 7.28, 14.2, 27.3, 51.6 mg/L). 100% immobilization was observed in 100 mg/L (mean measured concentration: 91.9 mg/L)
- Results with reference substance (positive control):
- The 24hr-EC50 value (95% confidence limits) of Potassium dichromate to Daphnia magna were determined 1.83 mg/L (1.60-2.14 mg/L).
- Reported statistics and error estimates:
- EC50 value with 95% confidence limits and NOEC (No observed effected concentration) were analyzed by CETIS Version 1.8.7.15 (Tidepool Scientific Software, USA). Binomial/Graphical methods were applied to obtain the effective concentrations and Steel Many-One Rank Sum test were used for NOEC in this study.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The 48-hr EC50 value (95% confidence limit) of Titanium citrate in Daphnia magna was 68.9 mg/L (51.6-91.9 mg/L), expressed in terms of the geometric mean measured concentration.
- Executive summary:
The acute toxicity of Titanium citrate to Daphnia magna was studied according to OECD 202 “Daphnia sp., Acute Immobilization Test”. The test substance was soluble in dilution water and it was possible to prepare 100 mg/L of test
solution (highest concentration) by direct addition method. Titanium was analyzed for determination of test concentration and the concentrations of test solutions were calculated using measured concentration of titanium.
According to the stability test, the concentration was 101.4-102.9% of initial concentration. Therefore, the toxicity test was performed under static system.
The range-finding test was conducted at the nominal concentrations of 0.1, 1, 10 and 100 mg/L by static system. No immobilization was observed in 0.1-10 mg/L and 100% immobilization was observed in 100 mg/L of test solution. Therefore, the definitive test was performed with a control and nominal concentrations of 9.6, 17.2, 30.9, 55.6, 100 mg/L using a static system. The definitive test was performed for 48 hours and 20 daphnids were exposed for each
concentration with four replicates. The mean measured concentrations were 7.28, 14.2, 27.3, 51.6, 91.9 mg/L (0.66, 1.29, 2.48, 4.69, 8.36 mg/L as titanium) for nominal concentrations of 9.6, 17.2, 30.9, 55.6, 100 mg/L
during test period.
During 48 hours’ test period, no immobilization and toxic symptoms were observed in control and 9.6, 17.2, 30.9 and 55.6 mg/L of test solution (mean measured concentration: 7.28, 14.2, 27.3, 51.6 mg/L (0.66, 1.29, 2.48, 4.69 mg/L as titanium)) and 100% immobilization was observed in 100 mg/L (mean measured concentration: 91.9 mg/L (8.36 mg/L as titanium)).
The 48-hr EC50 value (95% confidence limit) of Titanium citrate in Daphnia magna was 68.9 mg/L (51.6-91.9 mg/L), expressed in terms of the geometric mean measured concentration.
Reference
Exposure time |
24-hour |
48-hour |
EC50 values |
68.9 |
68.9 |
95% confidence limits |
51.6-91.9 |
51.6-91.9 |
NOEC |
51.6 |
51.6 |
Unit: mg/L, geometric mean measured concentrations)
Cumulative immobilization of Daphnia magna
Nominal concentration (mg/L) |
Mean measured concentration (mg/L) |
No. of animals tested |
Cumulative No. of immobilized daphnids (Initial population: 5 daphnids/replicate) |
|||||||||||
|
|
|
24-hour |
48-hour |
||||||||||
|
|
|
R1 |
R2 |
R3 |
R4 |
Total |
% |
R1 |
R2 |
R3 |
R4 |
Total |
% |
Control |
ND |
20 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
9.6 |
7.28 |
20 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
17.2 |
14.2 |
20 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
30.9 |
27.3 |
20 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
55.6 |
51.6 |
20 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
100 |
91.9 |
20 |
5 |
5 |
5 |
5 |
20 |
100 |
5 |
5 |
5 |
5 |
20 |
100 |
Rx : Replicate Number
ND: Not detected
Symptoms of intoxication of the test item toDaphnia magna
Nominal concentration (mg/L) |
Mean measured concentration (mg/L) |
Symptoms of Intoxication |
|
|
|
24-hour |
48-hour |
Control |
ND |
NOR (20) |
NOR (20) |
9.6 |
7.28 |
NOR (20) |
NOR (20) |
17.2 |
14.2 |
NOR (20) |
NOR (20) |
30.9 |
27.3 |
NOR (20) |
NOR (20) |
55.6 |
51.6 |
NOR (20) |
NOR (20) |
100 |
91.9 |
- |
- |
( ) : Number of daphnids
ND: Not detected
NOR: Normal
Measured concentrations of the test item in the test solution
Nominal concentration (mg/L) |
Measured concentration (mg/L) |
Mean measured concentration (mg/L) |
|
|
0-hour |
48-hour |
|
Control |
ND |
ND |
NA |
9.6 |
7.85 (81.8) |
6.75 (70.3) |
7.28 (75.8) |
17.2 |
14.6 (84.9) |
13.9 (80.8) |
14.2 (82.6) |
30.9 |
26.6 (86.1) |
28.1 (90.9) |
27.3 (88.3) |
55.6 |
50.8 (91.4) |
52.4 (94.2) |
51.6 (92.8) |
100 |
91.9 (91.9) |
- |
91.9 (91.9) |
ND: Not detected
NA: Not available
( ) : % of nominal concentration
- Test solution was not analyzed because all daphnids were dead
Description of key information
At 100 mg/l, immobilisation was observed, but at low concentrations tested, there was limited effect
Under environmental conditions, diluted titanium citrate will dissociate leading to the formation of insoluble titanium salts such as carbonates, oxide and hydroxide.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 68 mg/L
Additional information
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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