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EC number: 403-080-9 | CAS number: 92484-48-5 BENZTRIAZOL UV ABSORBER BUK 4499; BUK 4499; UV ABSORBER BUK 4499
- 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 aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1997-09-30 to 1997-10-03
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- edition 1993
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- Commission Directive 92/69/EEC (edition 1992)
- Deviations:
- no
- Principles of method if other than guideline:
- NA
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
NA - Analytical monitoring:
- yes
- Details on sampling:
- All test medium samples for the analytical determinations were taken from the test vessels (after mixing the medium) and kept at -18°C to - 25°C until analysis.
- Vehicle:
- no
- Details on test solutions:
- - Stock solution: 200.1 mg test substance was mixed with about 200 mL test medium in a breaker, mixed and filled up to 1000 mL with test medium.
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Pseudokirchnerella subcapitata
- Strain: 61.81
- Source (laboratory, culture collection): Sammlung von Algenkulturen, Pflanzenphysiologisches Institut der Universität Göttingen, D-37073 Göttingen
- Method of cultivation: under standardised conditions according to the test guidelines. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Post exposure observation period:
- NA
- Hardness:
- NA
- Test temperature:
- 22.5 - 23.5 °C
- pH:
- pH (Start) = 7.2 - 7.7
pH (End) = 7.2 - 9.5 - Dissolved oxygen:
- NA
- Salinity:
- NA
- Nominal and measured concentrations:
- Nominal concentrations: 0.9, 1.9, 4.3, 9.4, 21, 45 and 100 mg test substance/L
Measured concentrations: 2.1, 4.5, 9.6, 20.9, 45.5, 101.6 mg test substance/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer flasks, each with 50 mL algal suspension
- Nominal cells density: 10000 cells per mL test solution (+/-10%)
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- Light intensity and quality:101 µE/m2sec in the spectral range of 400 to 700 nm - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 34 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 30.7 - 37.9
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 4.3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 12 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 8.5 - 14.8
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 1.6 - 4.8
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.9 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 4.3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 8.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 7.3 - 10.3
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 9.4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- Due to the results of a pre-test the nominal concentrations of test item for the main test were selceted as 0.9, 1.9, 4.3, 9.4, 21, 45 and 100 mg test substance/L. Additionally, a blank control without test substance was tested.
During the test the actual test concentrations in the analysed test media were in the range of 98.57 - 126.32 % of the nominal values.
Consequently, the EC-values were calculated from the nominal concentrations. - Results with reference substance (positive control):
- The EbC50 for potassium dichromate after 72 hours of exposure was determined amoung 16 laboratories in an international ring-test with Scenedesmus subspicatus and Pseudokirchnerella subcapitata and found to be at 0.53 mg/L (0.20 to 0.75 mg/L) (reference control at July 11, 1997: EbC50 = 0.60 mg/L).
- Reported statistics and error estimates:
- The inhibition of algal growth was calculated as EC10 and EC50 (inclusive the 95 % confidence limits) for the biomass b (area under the growth curves) and for specific growth rates µ. The NOEC was determined by testing the mean biomass and mean growth rates of the test concentrations on significant differents to the respective control values (Dunnett-Test).
- Validity criteria fulfilled:
- yes
- Conclusions:
- The EC50 (72 h, Pseudokirchnerella subcapitata ) based on growth rate was determined to be 34 mg/L (95% confidence limit 30.7 - 37.9). The NOEC (growth rate, 72 h; Pseudokirchnerella subcapitata) was 4.3 mg/L.
The EC50 (72 h; Pseudokirchnerella subcapitata) based on biomass was determined to be 12 mg/L (95% confidence limit 8.5 - 14.8). The NOEC (biomass, 72 h; Pseudokirchnerella subcapitata) was 1.9 mg/L. - Executive summary:
The toxicity of sodium 3(2H-benzotriazol-2-yl)-5-sec-butyl-4-hydroxybenzenesulfonate towards green algae Pseudokirchnerella subcapitata was assessed for a 72 hours exposue according to EU method C.3 and OECD guideline 201. Due to the results of a pre-test the nominal concentrations of test item for the main test were selceted as 0.9, 1.9, 4.3, 9.4, 21, 45 and 100 mg test substance/L. Additionally, a blank control without test substance was tested. During the test the actual test concentrations in the analysed test media were in the range of 98.57 - 126.32 % of the nominal values. Consequently, the EC-values were calculated from the nominal concentrations. The EC values based on the nominal concentrations were calculated as follows:
Endpoint
Critical effect concentrations (mg/L; 0-72 h)
95% confidence limit
EC50 (biomass)
12
8.5 – 14.8
EC10 (biomass)
3.2
1.6 – 4.8
LOEC (biomass)
4.3
NOEC (biomass)
1.9
EC50 (growth rate)
34
30.7 – 37.9
EC10 (growth rate)
8.8
7.3 – 10.3
LOEC (growth rate)
9.4
NOEC (growth rate)
4.3
The positive control (potassium dichromate) revealed a EbC50 of 0.6 mg/L, which was well within the expected range of 0.2 - 0.75 mg/L and demostrated the validity and sensitively of the test.
Reference
NA
Description of key information
EC50(72h) = 34 mg/L for growth rate inhibition of Pseudokirchneriella subcapitata (OECD 201)
NOEC(72h) = 4.3 mg/L for growth rate inhibition of Pseudokirchneriella subcapitata (OECD 201)
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 34 mg/L
- EC10 or NOEC for freshwater algae:
- 4.3 mg/L
Additional information
The toxicity of sodium 3(2H-benzotriazol-2-yl)-5-sec-butyl-4-hydroxybenzenesulfonate towards green algae Pseudokirchnerella subcapitata was assessed for a 72 hours exposure according to EU method C.3 and OECD guideline 201. Due to the results of a pre-test the nominal concentrations of test item for the main test were selceted as 0.9, 1.9, 4.3, 9.4, 21, 45 and 100 mg test substance/L. Additionally, a blank control without test substance was tested. During the test the actual test concentrations in the analysed test media were in the range of 98.57 - 126.32 % of the nominal values. Consequently, the EC-values were calculated from the nominal concentrations. The EC50 (72 h) based on growth rate was determined to be 34 mg/L (95% confidence limit 30.7 - 37.9). The NOEC (growth rate, 72 h) was 4.3 mg/L.
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