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EC number: 308-766-0 | CAS number: 98283-67-1
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- adult fish: sub(lethal) effects
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 30 Dec 1994 - 27 Jan 1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- refer to category justification provided in IUCLID section 13
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 204 (Fish, Prolonged Toxicity Test: 14-day Study)
- Deviations:
- yes
- Remarks:
- The total wet weight of the fish for each concentration was determinded. The individual length or wet weight was not determined / The total length was determined instead the standard length.
- Qualifier:
- according to guideline
- Guideline:
- other: EEC Ring test of a method of determining the effects of chemicals on the growth rate of fish (1989)
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: approx. 1 L of water was taken from the controls and treatments in glass bottles. 57 mL 27% formol was added.
- Sample storage conditions before analysis: stored in glass bottles in the refrigerator - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Seven stock solutions were prepared in Milli-Q-water (210, 387, 682, 1160, 2220, 3790, 6610 mg/250 mL). Stock solutions were stored in a refrigerator and renewed on day 2, 5, 11, 16, 18 and 21. Before use they were stirred and warmed up to dissolve the test substance.
- Controls: DSWL prepared from ground water was for the controls - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Zebrafish
- Source: M.B. Ruysbroek B.V. (Noordvliet 159, Maassluis)
- Length at study initiation (length definition, mean, range and SD): 2.55 +/- 0.23 cm
- Weight at study initiation (mean and range, SD): 0.12 +/- 0.03 g
- Feeding during test
- Food type: artemias
- Frequency: daily - Test type:
- flow-through
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 28 d
- Hardness:
- not stated
- Test temperature:
- 24.1 - 25.5 °C
- pH:
- 7.8 - 8.2
- Dissolved oxygen:
- 7.2 mg/L
- Nominal and measured concentrations:
- Nominal concentrations: control, 0.18, 0.32, 0.56, 1.0, 1.8, 3.2, 5.6 mg/L
Measured concentrations:
- control (< 0.1 mg/L), 0.18 (0.2 mg/L), 0.32 (0.5 mg/L), 0.56 (0.7 mg/L), 1.0 (1.3 mg/L), 1.8 (2.2 mg/L), 3.2 (3.9 mg/L), 5.6 (3.1 mg/L) on 1995-01-02
- control (< 0.1 mg/L), 0.18 (0.3 mg/L), 0.32 (0.4 mg/L), 0.56 (0.7 mg/L), 1.0 (1.4 mg/L), 1.8 (2.5 mg/L), 3.2 (4.2 mg/L) on 1995-01-09
- control (0.1 mg/L), 0.18 (0.1 mg/L), 0.32 (0.1 mg/L), 0.56 (0.2 mg/L), 1.0 (0.5 mg/L), 1.8 (0.7 mg/L), 3.2 (1.7 mg/L) on 1995-01-16
- control (0.1 mg/L), 0.18 (0.2 mg/L), 0.32 (0.3 mg/L), 0.56 (0.5 mg/L), 1.0 (0.9 mg/L), 1.8 (1.9 mg/L), 3.2 (2.8 mg/L) on 1995-01-23 - Details on test conditions:
- TEST SYSTEM
- Test vessel: Glass chambers in the flow-through system
- Fill volume: 2.64 L
- Aeration: slightly aerated
- Type of flow-through: Flow-through system according to Van Leeuwen et. al. (1988)
- Renewal rate of test solution (frequency/flow rate): every 60 min
- No. of organisms per vessel: 16
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: synthetic medium from ground water
- Total organic carbon: 2.1, 2.0, 1.9 mg/L (medium was prepared three times on amounts of 10000 L each)
- Intervals of water quality measurement: weekly and at the beginning and at the end of the test
OTHER TEST CONDITIONS
- Photoperiod: 16 h light and 8 h dark
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2 - Reference substance (positive control):
- no
- Duration:
- 28 d
- Dose descriptor:
- LC50
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality
- Remarks on result:
- other: 3.2 - 4.6 mg/L
- Duration:
- 28 d
- Dose descriptor:
- other: LC100
- Effect conc.:
- 5.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- other: growth
- Details on results:
- - Concentrations that produce lethal or other effects: The concentrations 3.2 and 5.6 mg a.i./L produced lethal effects. From day 7 the test species exposed to 1.8 and 3.2 mg a.i./L appeared to take up less food. But the length and weight did not deviate from the control.
- Cumulative mortality at each concentration and for each recommended observation time if possible (based on an analytical purity of the test substance of 100%): no mortality up to 1.8 mg a.i./L, one fish died on day 7 at 3.2 mg a.i./L, 100% mortality on day 3 at 5.6 mg a.i./L
- Mortality in the controls: 0%
- Behavioural observation of the fish (based on an analytical purity of the test substance of 100%): From day 7 the test species exposed to 1.8 and 3.2 mg a.i./L appeared to take up less food. But the length and weight did not deviate from the control. - Reported statistics and error estimates:
- The log-logistic concentration response model of Van der Hoeven (1991) was used for the calculation of the LC50. The maximum likelihood of 1.6 mg/L was close to the confidence interval of 3.2 - 4.6 mg a.i./L.
Reference
The mortality was 100% after 2 days at the highest test concentrations of 5.6 mg a.i./L. At a concentration of 3.2 mg a.i./L a 50% mortality was observed after 28 days (LC50). The NOEC was in between 1 mg a.i./L (endpoint: condition) and 3.2 mg a.i./L (endpoint: growth).
Description of key information
NOEC (28 d) = 1.8 mg a.i./L, based on mortality of Danio rerio (OECD 204); read across (CAS 110615-47-9)
Key value for chemical safety assessment
Additional information
No data are available on the long-term toxicity of D-Glucopyranose, oligomeric, undecyl glycoside (CAS 98283-67-1) to fish. In accordance to Regulation (EC) No 1907/2006 Annex XI, 1.5 a read across was conducted to the structurally related category member substance D-Glucopyranose, oligomeric, C10-16-alkyl glycosides (CAS 110615-47-9). The read across approach is justified in the overall summary (IUCLID Chapter 6.1) and in detail in the category justification document attached in IUCLID Section 13.
In the study by TNO Institute of Environmental Sciences (1995), which was chosen as key study, the long-term toxicity to the zebrafish Brachydanio rerio was investigated in a prolonged fish toxicity test according to the OECD guideline 204 and GLP for 28 days (instead of 14 d). Therefore, the test can be considered as a long-term test. Additionally, parameters like behavior and growth were studied (according to “Guidance Document on Aquatic Ecotoxicology” published by the European Commission, 2002). The test resulted in a NOEC (28 d) of 1.8 mg a.i./L for the endpoint mortality and a NOEC (28 d) of 3.2 mg a.i./L based on growth.
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