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EC number: 813-543-0 | CAS number: 73984-93-7
- 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
Short-term toxicity to fish
Administrative data
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1985
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- GLP guideline study on supporting substance. The definitive test concentrations exceeded the level of water solubility of the test substance. After addition and mixing of the test substance to the test chambers an oily surface film and yellow oily droplets were observed on the bottom of the test chembers. There was no analytical monitoring of test concentrations therefore the results are based on nominal concentrations. This result is read-across from ‘1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-nonanethiol’. Read-across is justified as the two substances ‘1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-dodecanethiol’ and ‘1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-nonanethiol’ are virtually the same: the only difference between those two UVCB substances is that one of the used raw materials (alkanethiol) has a diversity in the C-range, i.e. on the one hand a tert. C12-alkanethiol is used in the manufacturing process, on the other hand a tert. C9. Hence, based on the (structural) similarity of both substances it is safe to say that the physicochemical, toxicological and ecotoxicological properties are likely to be similar.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Deviations:
- not specified
- GLP compliance:
- yes
Test material
- Reference substance name:
- 1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-nonanethiol
- EC Number:
- 293-927-7
- EC Name:
- 1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-nonanethiol
- Cas Number:
- 91648-65-6
- Molecular formula:
- not applicable (UVCB substance)
- IUPAC Name:
- 1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-nonanethiol
- Test material form:
- liquid: viscous
- Details on test material:
- - Description: viscous amber liquid
- Storage condition of test material: ambient, dark
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
No surrogate or analogue material was used.
Sampling and analysis
- Analytical monitoring:
- no
- Details on sampling:
- - Nominal concentrations: 100, 180, 320, 560 and 1000 mg/L
Test solutions
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test compound was weighed directly into the test chambers. Before addition to the chambers, 1.5 mL of dimethylformamide (DMF) was added to each sample weight to increase the dispersion of the compound in the dilution water. The solvent control received an aliquot (1.5 mL) of DMF equivalent to that used in the test concentrations. After addition and mixing of the test compound into the test chambers, an oily surface film and large yellow oily droplets were observed on the bottom of all test chambers. The amount of surface film and the size of the droplet on the bottom increased with increasing test concentration. These observations were the same after 96-hours of testing.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): dimethylformamide
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)): 0.01 %
Test organisms
- Test organisms (species):
- Pimephales promelas
- Details on test organisms:
- TEST ORGANISM
- Common name: Fathead minnow
- Source: in-house culture (Lot No. 485)
- Length at study initiation: 24 +/- 1.1mm
- Weight at study initiation: 0.20 +/- 0.034g
- Feeding during test: no
ACCLIMATION
- Acclimation period: 14 days
- Acclimation conditions: same as in the experimental part
- Type and amount of food: Standard commercial fish food (Rangen's)
- Feeding frequency: daily up until 48h prior to test initiation
- Health during acclimation: acclimation mortality reported as 1 %
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Post exposure observation period:
- No post exposure observation period described.
Test conditions
- Hardness:
- 40 - 45 mg/L as CaCO3
- Test temperature:
- 22 +/- 1 °C
- pH:
- 7.1 - 7.8
- Dissolved oxygen:
- 7.1 - 9.5 mg/L (82 % - 108 % saturation)
- Salinity:
- Not applicable.
- Nominal and measured concentrations:
- Nominal concentration
Range finding test: 1, 10 and 100 mg/L
Definitive test: 100, 180, 320, 560 and 1000 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 5 gallon glass vessels
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- No. of vessels per vehicle control (replicates): 1
- Biomass loading rate: approximately 0.13 g fish per litre
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: on-site well water
- Metals: aluminium < 0.010 ppm, arsenic < 0.0005 ppm, cadmium < 0.002 ppm, chromium < 0.006 ppm, cobalt < 0.003 ppm, copper < 0.002 ppm, iron < 0.004 ppm, lead 0.017 ppm, mercury 0.0008 ppm, nickel < 0.013 ppm, silver < 0.0004 ppm, zinc 0.001 ppm
- Pesticides: less than minimum detectable limits
- Alkalinity: 30-35 mg/L as CaCO3
- Intervals of water quality measurement: 0, 48, 96 h
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16h light/ 8h dark
TEST CONCENTRATIONS
- Spacing factor for test concentrations: logarithmic
- Test concentrations (Range finding study): 1, 10 and 100 mg/L
- Results used to determine the conditions for the definitive study: no mortalities at the highest concentration in the preliminary study therefore this was used as the lowest concentration in the definitive study - Reference substance (positive control):
- yes
- Remarks:
- Antimycin A
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 96 h
- Dose descriptor:
- LL50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Duration:
- 96 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- - Observations on body length and weight: length 24 +/- 1.1 mm and weight 0.20 +/- 0.034 g
- Other biological observations: none reported
- Mortality of control: none
- Other adverse effects control: none
- Abnormal responses: none
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: Not applicable since only nominal valuesare reported. - Results with reference substance (positive control):
- - Results with reference substance valid: Yes
- Mortality: 100 % mortality at 48h
- LC50(96h): 53 ng/L - Reported statistics and error estimates:
- LC50 values (for the positive control only) were calculated using either the binomial method or the probit method.
Any other information on results incl. tables
- Sublethal observations / clinical signs:
Table 1: Results for the test Substance
Test Conc. mg/L
Mortality
24h
48h
72h
96h
Control
0
0
0
0
Solvent control
0
0
0
0
100
0
0
0
0
180
0
0
0
0
320
0
0
0
0
560
0
0
0
0
1000
0
0
0
0
LL50(mg/L)
>1000
>1000
-
>1000
Table 2: Results for the Positive Control
Test Conc. mg/L
Mortality
24h
48h
72h
96h
Control
0
0
0
0
Solvent control
0
0
0
0
0.000014
0
0
0
0
0.000024
0
0
0
0
0.000042
0
0
0
0
0.000075
2
10
-
-
0.00014
7
10
-
-
LL50(mg/L)
0.11 x 10-5
5.6 x 10-5
-
5.3 x 10-5
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- Validity criteria were fulfilled.
- Conclusions:
- The test report describes a valid guideline study, conducted with GLP compliance. Based on the observed LL50 (equivalent to LC50) > 1000 mg/L, the test substance can be considered as non-toxic towards fish after an exposure time of 96 h.
- Executive summary:
A study was performed to assess the acute aquatic toxicity of the supporting substance '1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-nonanethiol' (CAS 91648-65-6). The method followed OECD Guideline 203, with the exception that the nominal concentrations were not measured analytically for confirmation. The preliminary 96 h acute toxicity study was conducted with the Fathead minnow at nominal test concentrations of 1, 10 and 100 mg/L. Ten fish per test concentration were used in the preliminary and the definitive study. In the definitive study test concentrations of 100, 180, 320, 560 and 1000 mg/L were tested. In parallel a control, a solvent control and a positive control group were tested. No mortality occurred at any of the test concentrations. Under the conditions of the test the LL50 at 96 hours exposure was determined to be > 1000 mg/L, whereat the result should be also applicable for the long-chain homologue '1,3,4-Thiadiazolidine-2,5-dithione, reaction products with hydrogen peroxide and tert-dodecanethiol' (no CAS#, no EC#).
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