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EC number: 230-191-8 | CAS number: 6969-71-7
- 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
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:
- 2010
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 1,2,4-triazolo[4,3-a]pyridin-3(2H)-one
- EC Number:
- 230-191-8
- EC Name:
- 1,2,4-triazolo[4,3-a]pyridin-3(2H)-one
- Cas Number:
- 6969-71-7
- Molecular formula:
- C6H5N3O
- IUPAC Name:
- [1,2,4]triazolo[4,3-a]pyridin-3(2H)-one
- Details on test material:
- Batch number : 09-378
Preparation date : February 19, 2010
Expiry date : July 19, 2010
Storage conditions : Room temperature / dark conditions
Constituent 1
Test solutions
- Vehicle:
- yes
- Details on test solutions:
- The main test included five different concentrations of test item, namely 1.0, 3.2, 10.0, 31.6 and 100.0 mg/L.
The test medium was prepared as follows: prior to the start of the test, a stock solution of 100.0 mg/L was prepared by direct weighing into reconstituted water. The obtained solution showed brown insoluble particles, therefore it was mixed by the mean of a magnetic stirrer for about 48 hours to achieve the maximum solubilisation of test item and then it was filtered by a cartridge filter (pore diameter 0.45 um) to obtain a clear solution. The test concentrations were then prepared by taking adequate aliquots of obtained solution and diluting them in aerated reconstituted water.
A negative control with only reconstituted water was tested.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- A strain of the freshwater crustacean Daphnia magna Straus was originally supplied by the Italian Health Department (Istituto Superiore di Sanità) in September 2004. Since that time, the clone has been bred in ChemService laboratories in reconstituted water with the same characteristic to the water used in the tests (as for pH, main ions, and total hardness) and under temperature and light conditions identical to those of the tests. The daphnia breeding was daily fed with a fixed amount of green algae Pseudokirchneriella subcapitata (formerly Selenastrum capricornutum) cultivated in the ChemService Laboratory and with a suspension of the yeast Saccharomyces cerevisiae.
At the start of the test, the organisms used in the test were 6-24 hours old and were not first brood progeny.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 140 - 250 mg/L as CaCO3
- Test temperature:
- The incubation temperature was continuously monitored during the course of the study by the means of a data logger. The measured values ranged between 20.1 and 21.5 °C during the test period.
- pH:
- The pH of the test medium after preparation was in the range 7.41 – 7.98 for test item solutions and 7.30 for control, therefore, the pH of the test medium was not adjusted before the start of the test.
- Details on test conditions:
- The test was performed in 50 mL glass beakers filled with 40 mL of test medium. The beakers were covered with glass plates to reduce the loss of water and to avoid the entry of dust into the solutions.
For each test concentrations and for the control, 20 daphnids were used divided into four replicates of five daphnids each. The daphnids were randomly distributed to the test vessels at initiation of the test. The daphnid’s loading rate was greater than one daphnid per 2 mL of test solution. - Reference substance (positive control):
- yes
- Remarks:
- potassium chromate (in a test run on December 2009)
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Duration:
- 48 h
- Dose descriptor:
- IC50
- Effect conc.:
- 80.5 mg/L
- Nominal / measured:
- nominal
- Remarks on result:
- other: 45.2 – 123.4
- Results with reference substance (positive control):
- Effect of potassium dichromate on Daphnia magna:
24 h IC50 (mg/L) Confidence interval (95%, mg/L)
ChemService study 0.71 0.66 – 0.76
Reference data
(UNI EN ISO 6341/99) 0.6 – 2.1
Any other information on results incl. tables
At the end of test period, in the negative control 0% of immobilization was observed and no daphnid was found trapped on the test water surface. These values comply with the validity criteria of the test, that provide a maximum immobilization and/or a maximum number of daphnids trapped in to water surface of 10% in the control medium at the end of the test.
The obtained experimental results allowed to calculate the NOEC, the LOEC and the IC50at 24 and 48 h. The results are as follows:
Time |
NOEC (mg/L) |
LOEC (mg/L) |
24 h |
31.6 |
100.0 |
48 h |
3.2 |
10.0 |
Time |
IC50(mg/L) |
95% Confidence range (mg/L) |
24 h |
100.0 |
100.0 – 100.0 |
48 h |
80.5 |
45.2 – 123.4 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- IC50 24 h = 100.0 mg/L
IC50 48 h = 80.5 mg/L
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