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Diss Factsheets
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EC number: 400-390-6 | CAS number: 87787-67-5 FLEXSORB-SE
- 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
- Endpoint:
- sediment toxicity: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Exposures were conducted between the 16th May and 26th May 1996
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study conducted in accordance with generally accepted scientific principles, possibly with incomplete reporting or methodological deficiencies, which do not affect the quality of relevant results.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: Test was performed based on the Paris Commision Guideline "MAFF/ERT Harmonised Protocol. A sediment bioassay using an amphipod Corophium sp."
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- not required
- Details on sampling:
- Please see details on test conditions.
- Vehicle:
- no
- Details on sediment and application:
- Test conditions: Three replicates were prepared for each test material concentration and five replicates for the control. The volume (800 ml) of overlying artificial seawater was maintained throughout the study by addition of water purified by reverse osmosis to compensate for water lost by evaporation. Test organisms were added to the spiked and control sediments at a density of 20 per vessel.
- Test organisms (species):
- Corophium volutator
- Details on test organisms:
- A batch of amphipods freshly dug from the Anglesey coast, free of malformation and of good health, were obtained on the 3rd May 1996 and assigned a batch number of CV960010.
Stock amphipods were held in 13 litre storage vessels on sieved sediment/detritus obtained from the collection site. - Study type:
- laboratory study
- Test type:
- static
- Water media type:
- saltwater
- Type of sediment:
- natural sediment
- Limit test:
- no
- Duration:
- 10 d
- Exposure phase:
- total exposure duration
- Post exposure observation period:
- Not applicable.
- Hardness:
- Not recorded.
- Test temperature:
- Temperature was measured at intervals for the aqueous medium in each test vessel.
Temperature recorded: 14.8 - 15.1ºC (see appendix 3) - pH:
- pH was measured at intervals for the aqueous medium in each test vessel.
pH recorded: 8.14 - 8.40 (see appendix 2) - Dissolved oxygen:
- Dissolved oxygen values were measured at intervals for the aqueous medium in each test vessel.
Recorded values: 97.7 - 98.8 mg kg-1 (see appendix 1) - Salinity:
- Artificial seawater with a salinity of 30.5 g/l
- Ammonia:
- Not recorded.
- Nominal and measured concentrations:
- Five (nominal) concentrations at 100, 316.2, 1000, 3162.3 and 10000 mg/kg
- Details on test conditions:
- Dilution media: Artificial seawater (Tropical Marine, Germany) with salinity of 30.5 g/l and natural sediment obtained from the site of collection of the test organisms.
Test vessels: Tall form glass beakers, 1 litre capacity.
Test concentrations: Five concentrations at 100, 316.2, 1000, 3162.3 and 10000 mg/kg expressed as dry weight of sediment together with an untreated control were prepared. Aliquots of the test substance were added to 100 ml of artificial seawater. This was added to the wet sediment and mixed. Untreated controls were prepared in a similar way without the addition of test material.
Test conditions: Three replicates were prepared for each test material concentration and five replicates for the control. The volume (800 ml) of overlying artificial seawater was maintained throughout the study by addition of water purified by reverse osmosis to compensate for water lost by evaporation. Test organisms were added to the spiked and control sediments at a density of 20 per vessel.
Photoperiod: Ambient laboratory lighting.
Aeration: Air bubbled directly into artificial seawater via polypropylene tubing.
Observations: Test organisms were observed at intervals during the 10 days of the study with regard to swimming, behavior and mortality. At the end of the study the sediment was re-suspended and sieved and the mortality data were recorded.
Death criterion: Organisms which became opaque and were lying on the surface of the sediment during the study were recorded as mortalities. Organisms exhibiting no movement and failing to respond to tactile stimulus at the end of the study were recorded as mortalities. - Reference substance (positive control):
- no
- Duration:
- 10 d
- Dose descriptor:
- LC50
- Effect conc.:
- > 10 000 mg/kg sediment dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks on result:
- other: The 95% confidence range could not be determined.
- Details on results:
- The LC50 was found to be > 10000 mg/kg dry weight of sediment. There was an indication of dose response only at the highest concentrations.
The highest concentration of test material producing no observable effect was determined to be 3162.3 mg/kg, this being the highest concentration giving a mortality value below or equal to the acceptable normal distribution of control mortality (0-20%). None of the concentrations tested produced 100% mortality.
Amphipods at all concentrations tested, reached the sediment surface within 5 minutes of addition to the test vessels.
The pH values at day 0 for the highest concentration (10000 mg/kg dry sediment) of test material were outside the validity criteria, however, this was not thought to have significantly affected the final result. - Results with reference substance (positive control):
- Not applicable.
- Reported statistics and error estimates:
- The mortality data calculated at each observation period would normally be processed by a computer program using probit analysis, supplied by the National Swedish Environmental Protection Agency, to derive the median effect concentration (LC50) which killed 50% of the animals exposed to the test material together with 95% confidence limits. However, in this instance the data was inappropriate for such analysis.
- Validity criteria fulfilled:
- yes
- Conclusions:
- From this study the ten day LC50 value was found to be >10,000 mg kg-1 dry weight of sediment.
- Executive summary:
The Corophium volutator sediment reworker test was performed on the test substance based on the Paris Commision Guideline "MAFF/ERT Harmonised Protocol. A sediment bioassay using an amphipod Corophium sp."
The 10 day LC50 value for the test substance was found to be >10,000 mg/kg (dry weight) of sediment. The 95% confidence range could not be determined.
The sediment reworker is not included in any ecotoxicological classification system.
Reference
From the mortality data observed under these test conditions (Table 1 and Appendix 4) after 10 days exposure to the test material, an LC50 of >10000 mg/kg dry weight of sediment was found (Table 2).
Table1: Cumulative percentage mortality (%) data.
Concentration mg kg-1 |
Observed mortalities (%) |
0 |
10.0 |
100 |
13.3 |
316.2 |
15.0 |
1000 |
10.0 |
3162.3 |
15.0 |
10000 |
48.3 |
Table 2: Toxicity data
Time (days) |
LC50 mg kg-1 |
95% Confidence limits |
Slope function |
Regression |
Degrees of freedom |
Probability (%) |
10 |
>10,000 |
- |
- |
- |
- |
- |
See attached background material for Appendix 1 -4.
Description of key information
The Corophium volutator sediment reworker test was performed on the test substance based on the Paris Commision Guideline "MAFF/ERT Harmonised Protocol. A sediment bioassay using an amphipod Corophium sp."
The 10 day LC50 value for the test substance was found to be >10,000 mg/kg (dry weight) of sediment. The 95% confidence range could not be determined.
Key value for chemical safety assessment
- EC50 or LC50 for marine water sediment:
- 10 000 mg/kg sediment dw
Additional information
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