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EC number: 215-343-3 | CAS number: 1322-93-6
- 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

Biodegradation in water: screening tests
Administrative data
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2018-2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Version / remarks:
- Adopted July 17, 1992
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- Sodium diisopropylnaphthalenesulphonate
- EC Number:
- 215-343-3
- EC Name:
- Sodium diisopropylnaphthalenesulphonate
- Cas Number:
- 1322-93-6
- Molecular formula:
- C16H20O3S.Na
- IUPAC Name:
- sodium diisopropylnaphthalene-sulfonate
- Test material form:
- solid: particulate/powder
- Details on test material:
- white to off-white lumps
Constituent 1
Study design
- Oxygen conditions:
- anaerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): Effluent freshly obtained from a municipal sewage treatment plant: 'Waterschap Aa en Maas', 's-Hertogenbosch, The Netherlands, receiving predominantly domestic sewage
- Laboratory culture: /
- Method of cultivation: /
- Storage conditions: The filtrate was kept aerated until inoculation.
- Storage length: /
- Preparation of inoculum for exposure: /
- Pretreatment: /
- Concentration of sludge: 4 mL filtrate of secondary effluent per litre of final volume.
- Initial cell/biomass concentration: /
- Water filtered: yes
- Type and size of filter used, if any: Secondary effluent was filtered through a coarse filter paper, the first 200 mL were discarded. - Duration of test (contact time):
- 28 d
Initial test substance concentrationopen allclose all
- Initial conc.:
- 2 mg/L
- Based on:
- test mat.
- Initial conc.:
- 4 mg/L
- Based on:
- test mat.
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Test duration 28 days for the inoculum blank and test suspension
14 days for the procedure and toxicity control
Test bottles 250-300 mL BOD bottles with glass stoppers.
Milli-RO water Tap-water purified by reverse osmosis (Millipore Corp., Bedford, Mass., USA).
Stock solutions of mineral components
A) 8.50 g KH2PO4
21.75 g K2HPO4
67.20 g Na2HPO4.12H2O
0.50 g NH4Cl
dissolved in 1 litre Milli-RO water, pH 7.4 + 0.2
B) 22.50 g MgSO4.7H2O dissolved in 1 litre Milli-RO water.
C) 36.40 g CaCl2.2H2O dissolved in 1 litre Milli-RO water.
D) 0.25 g FeCl3.6H2O dissolved in 1 litre Milli-RO water.
Mineral medium 1 mL aliquots of solution (A) to (D) were mixed and made up to 1 litre with Milli-RO water. The concentration of dissolved oxygen was measured for control purposes. The mineral medium was left at test temperature to obtain an oxygen-saturated solution at the start of the test. Care was taken to ensure the solutions were not supersaturated with oxygen.
Test set up Inoculum blank: Containing only inoculum (no test item)
Procedure control: Containing reference item and inoculum
Test suspension: Containing test item and inoculum (applicable for both test concentrations)
Toxicity control: Containing reference item, test item at the lowest concentration and inoculum.
Number and groups of test bottles Individual BOD bottles were prepared for each measuring point, except that the bottles measured at the start were also
measured on day 7. Parallel groups were prepared to allow duplicate measurements of oxygen consumption at the test intervals.
Illumination The test bottles were protected from light.
Reference substance
- Reference substance:
- other: sodium acetate
Results and discussion
- Test performance:
- The pH values at the start of the test were between 7.4 and 7.5.
The temperature recorded in a vessel with Milli-RO water in the same room varied between 21 and 23°C, and complied with the requirements as laid down in the study plan.
% Degradationopen allclose all
- Parameter:
- % degradation (O2 consumption)
- Remarks:
- for the low test item concentration
- Value:
- 3
- St. dev.:
- 6
- Sampling time:
- 21 d
- Parameter:
- % degradation (O2 consumption)
- Remarks:
- for the high test item concentration
- Value:
- 2
- St. dev.:
- 0
- Sampling time:
- 21 d
- Details on results:
- The relative biodegradation values calculated from the O2 measurements performed during the test period revealed no biologically relevant biodegradation of CH04207 at the low and high concentration of CH04207 (mean value of 3% and 2%, based on ThOD, respectively).
In the toxicity control, more than 25% biodegradation occurred within 14 days (mean value of 25%, based on ThOD). Therefore, the test item was assumed not to inhibit microbial activity.
BOD5 / COD results
- Results with reference substance:
- In the procedure control, sodium acetate was degraded by at least 60% (82%) within 14 days
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- In conclusion, CH04207 was not readily biodegradable under the conditions of the closed bottle test performed presently.
- Executive summary:
The objectiveofthe studywasto evaluate the organic test item CH04207 for its ready biodegradability in an aerobic, aqueous medium with microbial activity introduced by inoculation of secondary effluent during a test period of 28 days.
The study procedure described in this report was based onthe OECD guideline No. 301 D, 1992.
CH04207 consisted of white to off-white lumps with a purity of >97%. The Theoretical Oxygen Demand (ThOD) of CH04207 was calculated to be 2.14 mg O2/mg based on the molecular formula. Nominal concentrations of 2 and 4 mg/L were tested. No correction was made for the purity or composition of the test item.
The following test set up was applied, with duplicate vessels for each time point:
· Inoculum blank (only inoculum, no test item);
· Procedure control (sodium acetate at 2 mg/L and inoculum);
· Test item (CH04207 at 2 mg/L and inoculum);
· Test item (CH04207 at 4 mg/L and inoculum);
· Toxicity control (sodium acetate at 2 mg/L, CH04207 at 2 mg/L and inoculum).
A clear and colourless stock solution was prepared by dissolving 50 mg test item in mineral medium. Magnetic stirring was used to accelerate dissolution of the test item in mineral medium and to obtain a homogeneous stock solution. Volumes of stock solution corresponding with the test concentrations were then combined with inoculum and mineral medium.
Measurements of the oxygen concentrations were performed at the start of the experiment (day 0) and on day 7, 14, 21 and 28.
The relative biodegradation values calculated from the O2measurements performed during the test period revealed no biologically relevant biodegradation of CH04207 at the low and high concentration of CH04207 (mean value of 3% and 2%, based on ThOD, respectively). The toxicity control showed that CH04207 did not inhibit microbial activity.
Since all criteria for acceptability of the test were met, this study was considered to be valid.
In conclusion, CH04207 is designated as not readily biodegradable.
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