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EC number: 237-430-5 | CAS number: 13780-39-7
- 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 soil microorganisms
Administrative data
- Endpoint:
- toxicity to soil microorganisms
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: One concentration tested. No exposure in soil
Data source
Reference
- Reference Type:
- publication
- Title:
- Aquatic ecotoxicity tests of some nanomaterials
- Author:
- Velzeboer I, Hendriks AJ, Ragas AM, Van de Meent D
- Year:
- 2 008
- Bibliographic source:
- PMID: 19086210, Environmental Toxicology and Chemistry 27(9):1942-7
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Soil micro-organisms
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Titanium dioxide
- EC Number:
- 236-675-5
- EC Name:
- Titanium dioxide
- Cas Number:
- 13463-67-7
- IUPAC Name:
- dioxotitanium
- Reference substance name:
- Rutile (TiO2)
- EC Number:
- 215-282-2
- EC Name:
- Rutile (TiO2)
- Cas Number:
- 1317-80-2
- IUPAC Name:
- dioxotitanium
- Details on test material:
- - Molecular formula (as other than submission substance): TiO2
- Molecular weight (as other than submission substance): 79.899 g/mol
- Smiles notation (as other than submission substance): [Ti](=O)=O
- InChl (as other than submission substance): InChI=1/2O.Ti/rO2Ti/c1-3-2
- Structural formula attached as image file (as other than submission substance): O=Ti=O
- TiO2 (Sigma Aldrich, Zwijndrecht, The Netherlands), ordered as 10% (w/w) dispersion in water.
Constituent 1
Constituent 2
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
JUSTIFICATION FOR READ ACROSS
In the present study the water was spiked with the analogue material titanium dioxide and thus with exactly the substance formed by hydrolysis of the titaium tetrachlorise (source chemical). As the additionally released hydrogen chloride fully dissociates, the substance itself will not reach the sediment/terrestrial environment except via direct exposure, which is not expected in quantities exceeding the soil buffering capacity. Chloride is non-toxic and with regard to the high natural background concentrations irrelevant. Thus additionally released hydrogen chloride should be disregarded.
In conclusion the test was conducted with the relevant transformation product.
Recalculation of the measured threshold values is required on an isomolar basis as the analogue material results from isomolar transformation of the target chemical.
Sampling and analysis
- Analytical monitoring:
- yes
Test substrate
- Vehicle:
- no
Test organisms
- Test organisms (inoculum):
- soil
Study design
- Total exposure duration:
- 7 d
Test conditions
- Details on test conditions:
- Soil bacteria were sampled at Demmerik (The Netherlands) and added to 10M sterile Bis-tris(2-(bis(2-hydroxyethyl)amino)-2-(hydroxymethyl)propane-1,3-diol at pH 7. After 24h of incubation, the samples were transferred into multiwell, gram-positive plates.
These plates contained one organic substrate in each well together with a tetrazolium violet redox dye.
During one week, the color development was measured every day with a plate reader. - Nominal and measured concentrations:
- 100 mg TiO2/L nominal
- Reference substance (positive control):
- no
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 7 d
- Dose descriptor:
- other: NOELR
- Effect conc.:
- >= 100 other: mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- respiration rate
- Remarks:
- detected colorimetrically using tetrazolium violet redox dye (Microtox® photometer )
- Remarks on result:
- other: Corresponds to 1.25 mmol/L
- Duration:
- 7 d
- Dose descriptor:
- other: NOELR
- Effect conc.:
- >= 237 other: mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- other: parent chemical titanium tetrachloride
- Basis for effect:
- respiration rate
- Remarks:
- detected colorimetrically using tetrazolium violet redox dye (Microtox® photometer )
- Remarks on result:
- other: Converted from 1.25 mmol/L on the basis of MW TiCl4 = 189.712 g/mol
- Duration:
- 7 d
- Dose descriptor:
- other: NOELR
- Effect conc.:
- >= 168 other: mg/l
- Nominal / measured:
- estimated
- Conc. based on:
- other: target compound titanium oxychloride
- Basis for effect:
- other: detected colorimetrically using tetrazolium violet redox dye (Microtox® photometer )
- Remarks on result:
- other: Converted from 1.25 mmol/L on the basis of MW TiOCl2 = 134.77 g/mol
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The test article exhibited no subacute toxic effects to soil micro-organisms in saturated solution together with undissolved microdisperse matter in excess
- Executive summary:
The subacute toxicity of nanoscaled titanium dioxide to soil micro-organisms was studied using bacteria sampled at Demmerik (The Netherlands). The limit test was conducted during 7 days. However no guideline protocol was followed, the experiment is well documented and meets generally accepted scientific standards. Thus the study is considered valid and conclusive.
The test organisms were exposed in aqueous solution to the analogue material titanium dioxide and thus to exactly the substance formed by hydrolysis of parent compound titanium tetrachloride via target chemical titanium oxychloride. Recalculation of the measured value was made on an isomolar basis as the analogue material results from isomolar transformation of the target chemical.
The insoluble test item was applied in a nominal loading rate of 100 mg/L. The loading is far above the water solubility of the test article, which is about 1 µg/L. No analytical dose verification was performed. Due to the multiwell plate exposure no separation of the test organisms and the test article, e.g. by precipitation is suggested. The respiration of the test organisms was detected colorimetrically using tetrazolium violet redox dye.
In the sole loading the test article exhibited no effect and a NOELR of ≥ 100 mg/L was derived. Thus the applied loading is considered a NOELR with no corresponding LOELR. On the basis of the molar test article loading the level for the parent chemical, titanium tetrachloride, was assessed to be ≥ 237 mg/L. On the basis of the molar test article loading the level for the target chemical, titanium oxychloride, was assessed to be ≥ 168 mg/L. No threshold concentration can be derived.
In conclusion the test article exhibited no subacute toxic effects to soil micro-organisms in saturated solution together with undissolved microdisperse matter in excess.
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