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Diss Factsheets
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EC number: 701-162-1 | 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
Bioaccumulation: aquatic / sediment
Administrative data
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1995-07-25 to 1995-10-24
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP study according a Japanese Guideline (no details given), well and detailed reported, deficiencies in translation from Japanese
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Japanese METI Guideline according Test methods for New Chemical Compounds
- GLP compliance:
- yes
Test material
- Reference substance name:
- 6-(3-tetrapropenyl-2,5-dioxopyrrolidin-1-yl)hexanoic acid
- EC Number:
- 800-770-5
- Cas Number:
- 1424148-99-1
- Molecular formula:
- C22H39NO4
- IUPAC Name:
- 6-(3-tetrapropenyl-2,5-dioxopyrrolidin-1-yl)hexanoic acid
- Details on test material:
- Purity: 100%
Lot No. OP 2/94
brown, viscous liquid
Mp -20 to -30 deg C
Bp 185 deg C
Water solubility: ambigous results
Methanol solubility: >100 g/L
Constituent 1
- Radiolabelling:
- no
Sampling and analysis
- Details on sampling:
- Sampling twice a week, in total 16 times for determination of substance concentration in water. 4 Samplings for the analysis of the test itemin fish (after 2, 4, 6 and 8 weeks after intial exposure (0 d). Sampling in control fish at begin and end of the test
Test solutions
- Vehicle:
- yes
- Details on preparation of test solutions, spiked fish food or sediment:
- Dsipersant HCO-40, test item and 20 times its volume of HCO-40 were kneaded together preparing a stock solution by dilution with ion exchange water of 2000 mg/L
Test organisms
- Test organisms (species):
- Cyprinus carpio
- Details on test organisms:
- Supply: Sugishima Fish Hatchery
Rearing for two days to remove fish with abnormalities, Acclimatization at 25 +/- 2 deg C applying a drug to remove parasites, afterwards rearing for 57d in flowing water
Body weight: average 25.2 g
Body length: 9.9 cm
Lipid content: average 3.5%
Feed: pellet shaped compound feed for carp
2 concentration groups with 11 fish at start of exposure
Control group: 5 fish
Study design
- Route of exposure:
- aqueous
- Test type:
- flow-through
- Water / sediment media type:
- natural water: freshwater
- Total exposure / uptake duration:
- 57 d
Test conditions
- Hardness:
- not given
- Test temperature:
- 25 +/- 2 deg C
- pH:
- not given
- Dissolved oxygen:
- 7.0 to 7.6 mg/L
- TOC:
- not given
- Details on test conditions:
- Quantity of test water: 579 L/d was supplied at 2 ml / min, 100l glas water tanks
- Nominal and measured concentrations:
- 1st concentration group: 0.6 mg/L
2nd concentration group: 0.06 mg/L - Details on estimation of bioconcentration:
- Measurement of the test item in the test water (sampling see above) and measurement in fish. Whole fish was cut in pieces and extracted with acetonitrile / phosphoric acid after homogenization. After the workup procedure, the test item was determinded with HPLC (see above)
Results and discussion
Bioaccumulation factoropen allclose all
- Type:
- BCF
- Value:
- 8.6 L/kg
- Basis:
- whole body w.w.
- Time of plateau:
- 14 d
- Calculation basis:
- steady state
- Remarks on result:
- other: test item conc. in fish
LODm (LOQm = 3*LODm) - Remarks:
- Conc.in environment / dose:0.6 mg/L (Group 1)
- Type:
- BCF
- Value:
- < 15 L/kg
- Basis:
- whole body w.w.
- Time of plateau:
- 14 d
- Calculation basis:
- steady state
- Remarks on result:
- other: Min. BCF (Group 1) based on the LOQm test item in fish and measured test item conc. in water is BCF=15
- Remarks:
- Conc.in environment / dose:0.6 mg/L (Group 1)
- Type:
- BCF
- Value:
- 25 L/kg
- Basis:
- whole body w.w.
- Time of plateau:
- 14 d
- Calculation basis:
- steady state
- Remarks on result:
- other: test item conc. in fish is < LODm
- Remarks:
- Conc.in environment / dose:0.06 mg/L (Group 2)
- Type:
- BCF
- Value:
- < 158 L/kg
- Basis:
- whole body w.w.
- Time of plateau:
- 14 d
- Calculation basis:
- steady state
- Remarks on result:
- other: Min. BCF (Group 2) based on the LOQm test item in fish and measured test item conc. in water is BCF=158
- Remarks:
- Conc.in environment / dose:0.06 mg/L (Group 2)
- Details on kinetic parameters:
- none available
- Metabolites:
- not monitored
- Results with reference substance (positive control):
- no reference substance used
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Tetra-PSCA has shown a low bioaccumulation potential in an 8 week Fish BCF test. Most concentrations in the fish were below the Limit of Quantification of the Analytical method (LOQ m) or even below the LOD m (Limit of Detection). Two concentrations of the test item in water were tested (0.6 and 0.06 mg/L) and of each group one BCF could be calculated: BCF=8.6 L/kg wwt for the concentration group 1 (water conc. 0.6 mg/L) and BCF=25 L/kg wwt for concentration group 2 (water conc. 0.06 mg/L). These both BCF are below the minimum BCF which can be calculated from the LOQm for test item concentration in fish which is 8.9 µg/g and the test water concentration of the two groups. The minimum BCF which can be reliably calculated are 15 L/kg wwt for Group 1 (water conc. 0.6 mg/L) respectively 158 L/kg wwt for Group 2 (water conc. 0.06 mg/L). This means that the BCF (Group 1) is < 15 L/kg wwt and <158 L/kg wwt (Group 2) as no fish concentrations were measured in this test which would result in a higher BCF as these minimum BCF.
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