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EC number: 231-043-5 | CAS number: 7420-89-5
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 08 NOVEMBER 2018 to 17 NOVEMBER 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- According to OECD 201 resp. EU C.3
- Deviations:
- yes
- Remarks:
- -temperature during pre-culture incubation was 22.6 – 24.3°C, not 21.0 - 24.0°C. As all validity criteria were met and exponential growth was observed in the blank control this was stated as uncritical!
- Principles of method if other than guideline:
- • The stock solutions to be autoclaved were autoclaved for 20 minutes instead of the required 15 minutes. This can be considered uncritical, as the goal of sterility is achieved.
• The pre-culture was prepared 5 days before the test start. As all validity criteria were met and exponential growth was observed in the blank control this was stated as uncritical.
• The temperature during pre-culture incubation was in the range 22.6 – 24.3°C, and therefore not in the desired range (21.0 - 24.0°C). As all validity criteria were met and exponential growth was observed in the blank control this was stated as uncritical. - GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Disodium 1,5-dihydroxypentane-1,5-disulphonate
- Cas Number:
- 7420-89-5
- Molecular formula:
- C5H10Na2O8S2
- IUPAC Name:
- Disodium 1,5-dihydroxypentane-1,5-disulphonate
- Reference substance name:
- Sodium sulfate
- Cas Number:
- 7757-82-6
- IUPAC Name:
- Sodium sulfate
- Reference substance name:
- Sodium hydrogen sulfite
- Cas Number:
- 7631-90-5
- IUPAC Name:
- Sodium hydrogen sulfite
Constituent 1
impurity 1
impurity 2
Sampling and analysis
- Analytical monitoring:
- yes
Test organisms
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- The culture of Desmodesmus subspicatus was obtained in January 2016 by MBM Sciencebridge GmbH (Institut für Pflanzenphysiologie of Universität Göttingen). The algae are kept as stock culture on solid agar at 2 - 8 °C. From the stock culture, a permanent culture was prepared. From an aliquot of the permanent culture, the pre-culture was prepared.
Study design
- Total exposure duration:
- 72 h
Test conditions
- Details on test conditions:
- For each treatment, 200 mL of the respective test item solution was mixed with the necessary amount of algal pre-culture (0.397 mL) to achieve a cell concentration of 2.6 *103 cells/mL. For the blank control, 350 mL nutrient medium was used instead of test item solution and mixed with the necessary amount of algal pre-culture (0.497 mL). In this mixture, the pH-value was measured.
The real cell concentration at the beginning of the test was measured with an electronic particle counter in the blank control solution. This measured value was used as start cell concentration for all replicates.
Samples for the analytical determination were taken before addition of algal pre-culture.
The test vessels were filled with 45 ± 1 mL of the respective test solution and incubated open (covered with perforated plastic foil acting as a stopper) for 72 hours, shaken on an orbital shaker to keep the algae in suspension. Before the start of incubation and every 24 hours, the cell number was determined with an electronic particle counter. After the test, samples for the analytical determination were taken, afterwards the pH value in treatments and blank control was measured again.
At the end of the test, the treatments were examined microscopically in order to assess the appearance of the algae and detect abnormalities (e.g. caused by the exposure to the test item).
The content of DOC in the test vessels was measured at the start and at the end of the test.
For elimination of the algal cells before analytical determination at the end of the test, samples were centrifuged. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate was used as positive control in a separate reference test.
Results and discussion
Effect concentrations
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.35 mg/L
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- Parameter Value 95% confidence interval
NOEC (Growth Rate)72 h < 0.09 mg/L --
NOEC (Yield) 72 h < 0.09 mg/L --
LOEC (Growth Rate) 72 h ≤ 0.09 mg/L --
LOEC (Yield) 72 h ≤ 0.09 mg/L --
72h ErC10 0.57 mg/L 0.33 – 0.98 mg/L
72h EyC10 n. d. --
72h ErC50 2.35 mg/L 1.25 – 4.35 mg/L
72h EyC50 0.23 mg/L 0.21 – 0.24 mg/L - Results with reference substance (positive control):
- The 72h-EC50 values of potassium dichromate were determined in a separate reference test. For the estimation of the 72h-EC50 values of the positive control, the fits showed sufficient statistical correspondence of the data with the dose-response-equation. The values were within the range of the laboratory.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Significant inhibition of algal growth was observed at all tested concentrations.
- Executive summary:
The study was performed using 5 concentrations ranging from 0.1 to 10 mg/L. Incubation time (test system Desmodesmus subspicatus) was 72 hours. The cell concentration of each replicate was determined by measuring the cell numbers every 24 hours with an electronic particle counter. Growth rate µ and the yield were determined from the cell number at the respective observation times.
Significant inhibition of algal growth was observed at all tested concentrations.
Due to the high inhibition values in the lowest concentration for the endpoint yield no EC10 could be determined and for both endpoints the LOEC and NOEC therefore was given as a range.
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