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EC number: 200-463-0 | CAS number: 60-23-1
- 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

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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Principles of method if other than guideline:
- Guidance document on aquatic toxicity testing of difficult substances and mixtures, OECD series on testing and assessment number 23, 2000. was also followed in this study.
- GLP compliance:
- yes
Test material
- Reference substance name:
- Mercaptamine
- EC Number:
- 200-463-0
- EC Name:
- Mercaptamine
- Cas Number:
- 60-23-1
- Molecular formula:
- C2H7NS
- IUPAC Name:
- mercaptamine
- Test material form:
- solid: particulate/powder
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Remarks:
- TOC analysis
- Details on sampling:
- It was not possible to develop a stable analytical method for the specific analysis of the test item. It was consequently decided to analyse the Total Organic Carbon (TOC) concentrations as a surrogate measure.
Samples for possible analysis were taken from all test concentrations and the control according to the schedule below from replicates without algae.
Frequency at t=0 h and t=72 h
Volume 40 mL
Storage Samples were stored in a refrigerator (2-8°C) until analysis.
Additionally, reserve samples of 40 mL were taken from all test solutions for possible analysis. If not used, these samples were stored in a refrigerator (2-8°C) for a maximum of three months after delivery of the draft report, pending on the decision of the sponsor for additional analysis.
At the end of the exposure period, the replicates without algae were not pooled at each concentration before sampling. Instead, the individual replicates were used to provide the samples to be analysed and the reserve samples, respectively.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- The batches of Mercaptamine tested were white powders with a purity of 98.8-99.4% and not completely soluble in test medium at the loading rates initially prepared.
For the range-finding test, preparation of test solutions started with a loading rate of 100 mg/L applying a three-day period of magnetic stirring to ensure maximum dissolution of the test item in test medium. Thereafter, the aqueous Saturated Solution (SS) was collected by filtration through a 0.45 µm membrane filter (RC55, Whatman). After adjusting the pH from 9.5 to 8.6 with 1 M HCl (Merck, Darmstadt, Germany), the collected fraction was used as the highest test concentration. Test medium without test item was filtered as well and the pH adjusted from 8.0 to 8.6 using 1 M NaOH (Merck, Darmstadt, Germany). Lower test concentrations were prepared by subsequent dilutions of the SS in test medium. All test solutions were clear and colorless at the end of the preparation procedure.
For the final test, preparation of test solutions started with loading rates individually prepared at 1.0, 3.2, 10, 32 and 100 mg t.i./L. A three-day period of magnetic stirring was applied to ensure maximum dissolution of the test item in test medium. Thereafter, the aqueous Water Accommodated Fractions were collected by filtration through a 0.45 µm membrane filter (RC55, Whatman). The pH of the filtrates resulting from the two highest loading rates was adjusted from 9.0-9.6 to 8.5 with 1 M HCl (Merck, Darmstadt, Germany). The pH of the filtrates resulting from the two lowest loading rates was adjusted from 8.2 to 8.5 using 1 M NaOH (Merck, Darmstadt, Germany). After the pH adjustments, the obtained solutions were used as test concentrations. Test medium without test item was filtered and the pH adjusted from 7.9 to 8.5 using 1 M NaOH (Merck, Darmstadt, Germany). Afterwards, the treated medium was used for the control group. All test solutions were clear and colorless at the end of the preparation procedure.
After preparation, volumes of 50 mL were added to each replicate of the respective test concentration. Subsequently, 1 mL of an algal suspension was added to each replicate providing a cell density of 10^4 cells/mL.
Any residual volumes were discarded.
Test organisms
- Test organisms (species):
- Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST SYSTEM
Species Pseudokirchneriella subcapitata, strain: NIVA CHL 1
Source In-house laboratory culture.
Reason for selection This system is a unicellular algal species sensitive to toxic items in the aquatic ecosystem and has been selected as an internationally accepted species.
FRESH WATER ALGAE CULTURE
Stock culture: Algae stock cultures were started by inoculating growth medium with algal cells from a pure culture on agar. The suspensions were continuously aerated and exposed to light in a climate room at a temperature of 21-24°C.
Light intensity: 60 to 120 µE/m2/s when measured in the photosynthetically effective wavelength range of 400 to 700 nm.
Stock culture medium: M1; according to the NPR 6505 (“Nederlandse Praktijk Richtlijn no. 6505”) formulated using Milli-RO water (tap-water purified by reverse osmosis; Millipore Corp., Bedford, Mass., USA) with the following composition:
Pre-culture 3 days before the start of the test, cells from the algal stock culture were inoculated in culture medium at a cell density of 1 x 104 cells/mL. The pre-culture was maintained under the same conditions as used in the test. The cell density was measured immediately before use.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Test temperature:
- 21 - 22 °C
- pH:
- 8.1 - 8.6
- Nominal and measured concentrations:
- WAF loading rates: 1.0, 3.2, 10, 32, 100 mg/L
Nominal TOC concentrations: 0.31, 1.0, 3.1, 10, 31 mg/L - Details on test conditions:
- Test Procedure and Conditions
Test duration : 72 hours
Test type: Static
Test vessels: 100 mL, all-glass, containing 50 mL of test solution
Medium: M2
Cell density: An initial cell density of 1 x 10^4 cells/mL.
Illumination: Continuously using TLD-lamps with a light intensity within the range of 68 to 73 µE.m-2.s-1.
Incubation: Capped vessels were distributed at random in the incubator and daily repositioned. During incubation the algal cells were kept in suspension by continuous shaking.
Controls: Test medium without test item or other additives.
Replicates: 3 replicates of each test concentration,
6 replicates of the control,
2 extra replicates of each test group without algae for sampling purposes at the end of the test,
1 replicate of each test concentration without algae background for the treated solutions for the determination of cell densities. - Reference substance (positive control):
- yes
- Remarks:
- not concurrent
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- 22 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Results with reference substance (positive control):
- Potassium dichromate:
The EC50 for growth rate inhibition (72h-ERC50) was 0.86 mg/L with a 95% confidence interval ranging from 0.84 to 0.88 mg/L. The historical ranges for growth rate inhibition lie between 0.82 and 2.3 mg/L. The observed 72h-ERC50 for the algal culture tested corresponds with this range.
Any other information on results incl. tables
Table 1: Growth Rate And Percentage Inhibition For The Total Test
Period
Mercaptamine WAF loading rate (mg t.i./L) |
Mean |
Std. Dev. |
n |
%Inhibition |
Control |
1.758 |
0.0097 |
6 |
|
1.0 |
1.698 |
0.0201 |
3 |
3.4# |
3.2 |
1.593 |
0.0141 |
3 |
9.4# |
10 |
1.214 |
0.0159 |
3 |
31* |
32 |
0.671 |
0.0070 |
3 |
62* |
100 |
0.360 |
0.0951 |
3 |
80* |
* effect was statistically significant;#effect statistically significant but biologically not relevant (<10%).
Table 2: Growth Rate And Percentage Inhibition At Different Time
Intervals
Mercaptamine WAF loading rate (mg t.i./L) |
n |
0 – 24 h |
24 – 48 h |
48 – 72h |
|||
Mean |
%Inhibition |
Mean |
%Inhibition |
Mean |
%Inhibition |
||
Control |
6 |
1.796 |
|
1.898 |
|
1.580 |
|
1.0 |
3 |
1.746 |
2.8 |
1.880 |
0.92 |
1.466 |
7.2 |
3.2 |
3 |
1.734 |
3.4 |
1.729 |
8.9 |
1.316 |
17 |
10 |
3 |
1.493 |
17 |
1.186 |
38 |
0.963 |
39 |
32 |
3 |
1.059 |
41 |
0.691 |
64 |
0.263 |
83 |
100 |
3 |
0.000 |
100 |
0.070 |
96 |
1.011 |
36 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The EL50 for growth rate inhibition (72h-ERL50) was 22 mg t.i./L with a 95% confidence interval ranging from 21 to 24 mg t.i./L. The 72h-NOEL for growth rate inhibition was 3.2 mg t.i./L based on biological relevance
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