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EC number: 211-802-7 | CAS number: 696-99-1
- 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:
- Sep. - Nov. 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Hess. Ministerium für Umwelt, Energie, Landwirtschaft und Verbraucherschutz, Wiesbaden, Germany
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
No test surrogate or analogue material were used. - Analytical monitoring:
- yes
- Details on sampling:
- The supporting TOC analyses at time t0 could not be performed on the same day of collection of the specimens. Therefore, these specimens from freshly prepared test solutions were stored at 2-8 °C for one day and then analysed.
- Vehicle:
- no
- Details on test solutions:
- Different amounts of the test item were dispersed in dilution water (Elendt M4 medium). The test item was introduced into the test solution in one step. The incubation period was 48hr.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Strain: STRAUS (clone 5)
- Source: Dr. M. Bergtold, BASF, D-67117 Limburgerhof; the strain originally derived from the Institut National de Recherche Chimique Appliquee, France in 1978 and cultivated since then at BASF
- cultivated in: medium M4 acc. Elendt
- Age at test initiation: less than 24 hr
- Method of breeding: transferred in new test medium at an interval of 1 to 3 days followed by feeding
- Feeding during test: no
- Type of food: Desmodesmus subspicatus- and/or Chlorella-cells - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- No details available.
- Test temperature:
- 20 ± 1 °C
- pH:
- at t0 / after 48 hr
control: 9.0 / 8.0
10 mg/L: 9.12 / 7.93
20 mg/L: 8.98 / 7.88
40 mg/L: 8.68 / 7.81
80 mg/L: 8.07 / 7.74
160 mg/L: 7.30 / 7.54 - Dissolved oxygen:
- O2-Content [mg O2/L]:
at t0: 7.92 ± 0.03
after 48 hr: 7.82 ± 0.03 - Salinity:
- No details available.
- Nominal and measured concentrations:
- nominal / measured concentrations:
10 mg/L / 5.39 mg/L
20 mg/L / 15.01 mg/L
40 mg/L / 33.30 mg/L
80 mg/L / 63.95 mg/L
160 mg/L / 131.98 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 50 mL beakers made of glass
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- medium: Elendt M4 medium
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16hr of light and 8hr of darkness
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
The effect of the test item on the animals was examined by the determination of the swimming behaviour of the daphnias. For this purpose the respective test vessel was gently agitated. Daphnia showing no swimming within 15 sec. were considered as immobile. Moving of antenna was not considered as swimming. Observation after 24 hr and 48 hr
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Range finding study
- Test concentrations: 1 mg/L, 10 mg/L, 100 mg/L and 1,000 mg/L
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 66.5 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 82.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- As a conclusion of the analytical part of this study, it must be stated that the concentrations of „(benzylamine)trifluoroboron“ decreased by 15% up to 68%: After 48 hr at 10 mg/L there was a recovery of 31.5% of the initial concentration measured a time t0. At 160 mg/L 85% of the initial concentration was measured after 48hr. Based on this, the reported effect concentrations (EC values) should refer to measured concentrations of the test item.
- Results with reference substance (positive control):
- In order to verify the sensitivity of the test system towards toxic items the effect of potassium dichromate towards different animals of this breed was tested prior to beginning of the test. The value of the EC50 (24hr) in this period of time was 0.84 mg/L potassium dichromate.
- Validity criteria fulfilled:
- yes
- Remarks:
- The validity criteria for the study as given by the OECD Guideline 202 were met.
- Conclusions:
- The study is regarded as a valid guideline study with certificated GLP compliance. The reported result for EC50 is 66.5 mg/L.
- Executive summary:
„(benzylamine)trifluoroboron“ was tested for acute toxicity towards daphnia according to OECD-Test Guideline 202 (version dated 13-Apr-2004). In order to investigate the influence of the test item towards the daphnias, the swimming behaviour of the animals was recorded. Under the conditions used for the test, immobilisation of the daphnias was observed at concentrations of the test item at concentrations 80 mg/L up to 160 mg/L active substance. Within the main test the test item was tested at concentrations 10 to 160 mg/L. The reported results for EC50 after 48 hr are 82.8 mg/L on basis of the nominal concentrations and 66.5 mg/L on basis of the measured concentrations.
As a conclusion of the analytical part of this study, it must be stated that the concentrations of „(benzylamine)trifluoroboron“ decreased by 15% up to 68%: After 48 hr at 10 mg/L there was a recovery of 31.5% of the initial concentration measured a time t0. At 160 mg/L 85% of the initial concentration was measured after 48hr. Based on this, the reported effect concentrations (EC values) should refer to measured concentrations of the test item.
The test is considered valid as all conditions for vylidity were met: In the control without any test item no dead animals were observed. In the test solutions the oxygen concentration did not drop below a value of 60% of the saturation value of approx. 5 mg/ O2/L.
Reference
Screening test
Nominal Concentration of the test item (mg/L) | Ratio immobilised Daphnia [%]1) | O2-Content [mg O2/L] |
Water Temperature [°C] | pH | ||||
24hr | 48hr | t0 | 48hr | t02) | 48hr2) | t0 | 48hr | |
Control (0) | 0 [0/10] | 0 [0/10] | 8.5 | 8.6 | 21.4 | 20.2 | 9.04 | 8.11 |
1 | 0 [0/10] | 0 [0/10] | 8.5 | 8.6 | 21.6 | 20.3 | 9.01 | 8.13 |
10 | 0 [0/10] | 0 [0/10] | 8.4 | 7.9 | 21.6 | 20.4 | 8.87 | 8.10 |
100 | 30 [3/10] | 80 [8/10] | 8.3 | 6.7 | 21.6 | 20.4 | 7.60 | 7.91 |
1000 | 100 [10/10] | 100 [10/10] | 8.3 | 8.5 | 21.6 | 20.4 | 3.53 | 3.36 |
1000 with pH-adjustment at time t0 | 80 [8/10] | 100 [10/10] | 8.3 | 8.4 | 21.5 | 20.4 | 7.19 | 6.91 |
1)Numbers
in brackets give the absolute numbers of immobilised animals at each concentration.
2)Temperatures
are higher than indicated in the study plan (20 ± 1 °C). This represents
a deviation
of the study plan which is not considered to have an influence on the
integrity of the
study.
Main test
Nominal Concentration of the test item (mg/L) | Ratio immobilised Daphnia [%]1) | O2-Content [mg O2/L] |
Water Temperature [°C]2) | pH | ||||
24hr | 48hr | t0 | 48hr | t0 | 48hr | t0 | 48hr | |
Control (0) | 0 [0/20] | 0 [0/20] | 7.94 | 7.81 | 21.0 | 21.4 | 9.00 | 8.00 |
10 | 0 [0/20] | 0 [0/20] | 7.95 | 7.80 | 21.0 | 21.4 | 9.12 | 7.93 |
20 | 0 [0/20] | 0 [0/20] | 7.91 | 7.80 | 20.9 | 21.4 | 8.98 | 7.88 |
40 | 0 [0/20] | 0 [0/20] | 7.90 | 7.81 | 21.0 | 21.4 | 8.68 | 7.81 |
80 | 0 [0/20] | 40 [8/20] | 7.94 | 7.84 | 21.0 | 21.4 | 8.07 | 7.74 |
160 | 15 [3/20] | 100 [20/20] | 7.90 | 7.85 | 21.0 | 21.4 | 7.30 | 7.54 |
1)Numbers
in brackets give the absolute numbers of immobilised animals at each concentration
2)Temperatures
are slightly higher than indicated in the study plan (20 ± 1 °C). This represents
a deviation of the study plan which is not considered to have an
influence on the
integrity of the study.
Description of key information
OECD 202, GLP, daphnia magna, static freshwater, LC50 = 66.5 mg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 66.5 mg/L
Additional information
„(benzylamine)trifluoroboron“ was tested for acute toxicity towards daphnia according to OECD-Test Guideline 202 (version dated 13-Apr-2004). In order to investigate the influence of the test item towards the daphnias, the swimming behaviour of the animals was recorded. Under the conditions used for the test, immobilisation of the daphnias was observed at concentrations of the test item at concentrations 80 mg/L up to 160 mg/L active substancet. Within the main test the test item was tested at concentrations 10 to 160 mg/L. The reported results for EC50 after 48 hr are 82.8 mg/L on basis of the nominal concentrations and 66.5 mg/L on basis of the measured concentrations.
As a conclusion of the analytical part of this study, it must be stated that the concentrations of „(benzylamine)trifluoroboron“ decreased by 15% up to 68%: After 48 hr at 10 mg/L there was a recovery of 31.5% of the initial concentration measured a time t0. At 160 mg/L 85% of the initial concentration was measured after 48hr. Based on this, the reported effect concentrations (EC values) should refer to measured concentrations of the test item. The validity criteria for the study as given by the OECD Guideline 202 were met.
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