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EC number: 231-964-2 | CAS number: 7782-78-7
- 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

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:
- 2010-03-15 to 2010-03-18
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study was performed and reported in compliance with the OECD Guideline 201, EC and German principles of GLP.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Statement of GLP compliance in report
Test material
- Reference substance name:
- Nitrosylsulphuric acid
- EC Number:
- 231-964-2
- EC Name:
- Nitrosylsulphuric acid
- Cas Number:
- 7782-78-7
- Molecular formula:
- HNO5S
- IUPAC Name:
- hydroxy(nitrosooxy)sulfane dioxide
- Test material form:
- other: liquid
- Details on test material:
- - Name of test material (as cited in study report): LZ5593
- Physical state: Viscous liquid
- Purity test date: 2009-11-20
- Expiration date of the lot/batch: 2011-11-20
- Storage condition of test material: Room temperature, protected from moisture and light.
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 6.25 - 12.5 - 25.0 - 50.0 - 100 mg/L and control
- Sampling method: The test item contains and partly hydrolyses to sulfuric acid. Thus, the total sulfuric acid content for all concentrations and the
control were analytically verified at the beginning and end (72 h) of the test via UV-spectrophotometry. Separate replicates for the test item analysis at test start were prepared (provided without alga). Samples at the end of the test were taken directly from the test replicates.
- Sample storage conditions before analysis: None, direct analysis
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution of 100 mg/L was freshly prepared with dilution water. Dispersion treatment was agitation.
- Eluate: Dilution water
- Differential loading: 6.25 - 12.5 - 25.0 - 50.0 - 100 mg/L
- Controls: Six replicates without test item were tested under the same test conditions as the test replicates.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): None
Test organisms
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: Desmodesmus subspicatus Chodat
- Strain: SAG 86.81
- Source (laboratory, culture collection): SAG Pflanzenphysiologisches Institut der Universitaet Goettingen, Nikolausberger Weg 18, D-37073 Goettingen, Germany
- Age of inoculum (at test initiation): 3 days
- Method of cultivation: Fresh stocks were prepared from Z-Agar. Light intensity amounted 35 - 70 µE x m-2 x s-1 for 24 h per day.
ACCLIMATION
- Culturing media and conditions (same as test or not): Same as test
- Any deformed or abnormal cells observed: No
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Post exposure observation period:
- None
Test conditions
- Hardness:
- Not measured
- Test temperature:
- Mean: 22 °C, Min: 21 °C, Max: 23 °C
- pH:
- Nominal test item concentration pH-value
[mg/L] Start; 0 h End; 72 h
100
pH-Control 7.84 7.11
100 2.94 2.96
50.0 3.52 3.54
25.0 6.22 5.40
12.5 7.04 7.29
6.25 7.29 7.35
Control 7.96 8.12 - Dissolved oxygen:
- Not measured
- Salinity:
- Not measured, freshwater
- Nominal and measured concentrations:
- Please refer to "Any other information on materials and methods incl. tables"
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 mL Erlenmeyer flasks
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: sterile 250 mL Erlenmeyer flasks, test volume 100 mL
- Aeration: Test containers were placed on a rotary shaker and oscillated at appr. 70 rpm
- Type of flow-through (e.g. peristaltic or proportional diluter): None
- Renewal rate of test solution (frequency/flow rate): One application at test start
- Initial cells density: 5074 cells/mL
- Control end cells density: Mean 1175645 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per vehicle control (replicates): None
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Dilution water, composition acc. to the guideline
- Hardness: 0.24 mmol Ca+Mg/L
- pH-value: 8.1 +/- 0.2
- Culture medium: Nutrient Medium Z acc. to LÜTTGE et al. (1994)
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: 24 h
- Light intensity and quality: 60 - 120 µE x m-2 x s-1
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: [counting chamber; electronic particle counter; fluorimeter; spectrophotometer; colorimeter] Fluorimeter, via Chlorophyll-a fluorescence (excitation at 436 nm, emission at 685 nm), cell concentrations were related to all cell density values acc. to a calibration curve.
TEST CONCENTRATIONS
- Range finding study: Yes
Results of the Range Finding Test (0-72 h)
Results of the Range Finding Tests (0-72 h)
Nominal
Test Item Concentration [mg/L] Specific Growth Rate Inhibition [%] Yield Inhibition [%]
100 100 100
10 - 4 - 19
1 - 6 - 32
0.1 - 6 - 35
0.01 - 6 - 34
100 (pH adjusted) 21 67
- Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 33 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: (31.7 – 34.2)
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test):
- Unusual cell shape: No
- Colour differences: No
- Flocculation: No
- Adherence to test vessels: No
- Aggregation of algal cells: No
- Other: No
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: No - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50:
Rate-related inhibition: 0.614 (CI 0.551 – 0.679) mg/L
Yield Inhibition: 0.333 (CI 0.318 – 0.350) mg/L - Reported statistics and error estimates:
- NOEC/LOEC was determined by calculation of statistical significance of growth rates and yield. As standard One Way Analysis of Variance (ANOVA) and DUNNETT’s Test were used for NOEC/LOEC calculations. When running a One Way Analysis of Variance a Normality test and an Equal Variance test were done first. The KOLMOGOROV-SMIRNOV-Test was used to test for normally distributed populations. P-values for both Normality and Equal Variance test were 0.05. The -value (acceptable probability of incorrectly concluding that there is a difference) is =0.05. Equal variance test failed for growth rate calculation. The data were transformed using Graph Pad Prism function
Y = Y sqrt.
Detection of statistically significant differences were considered negligible when inhibition values were ≤ 10 %. These findings were marked “biologically not significant”. Following the recommendations of the UBA (HEGER ET AL. 1998), inhibitions
> 10 % are significant. The findings were marked “biologically significant”.
Any other information on results incl. tables
NOEC, LOEC and EC - values of LZ5593(0-72 h)
based on nominal test item concentrations [mg/L]
Rate-related Inhibition |
|
NOEC |
25.0 |
LOEC |
50.0 |
ErC10 |
26.9 (26.0 – 28.1) |
ErC20 |
29.1 (28.1 – 30.4) |
ErC50 |
33.0 (31.7 – 34.2) |
Inhibition of Yield |
|
NOEC |
6.25 |
LOEC |
12.5 |
EyC10 |
6.25 |
EyC20 |
23.5 (22.2 – 24.7) |
EyC50 |
28.5 (27.2 – 29.8) |
Cell Densities
|
Nominal test item concentration |
Replicate |
Cell density [cells/mL] |
||||||
[mg/L] |
No. |
0 h |
24 h |
48 h |
72 h |
|
|||
100 |
1 |
5074 |
36734 |
194752 |
899866 |
|
|||
2 |
5074 |
38854 |
216962 |
950809 |
|
||||
3 |
5074 |
44098 |
224748 |
919583 |
|
||||
Mean |
5074 |
39895 |
212154 |
923419 |
|
||||
100 |
1 |
5074 |
d.l. |
d.l. |
3800 |
|
|||
2 |
5074 |
d.l. |
d.l. |
4180 |
|
||||
3 |
5074 |
d.l. |
d.l. |
3800 |
|
||||
Mean |
5074 |
d.l. |
d.l. |
3927 |
|
||||
50.0 |
1 |
5074 |
d.l. |
d.l. |
4560 |
|
|||
2 |
5074 |
d.l. |
d.l. |
3420 |
|
||||
3 |
5074 |
d.l. |
d.l. |
3420 |
|
||||
Mean |
5074 |
d.l. |
d.l. |
3800 |
|
||||
25.0 |
1 |
5074 |
36591 |
191034 |
803512 |
|
|||
2 |
5074 |
40191 |
205175 |
855045 |
|
||||
3 |
5074 |
39887 |
200574 |
937545 |
|
||||
Mean |
5074 |
38890 |
198928 |
865367 |
|
||||
12.5 |
1 |
5074 |
39194 |
203908 |
951235 |
|
|||
2 |
5074 |
39850 |
240886 |
1047409 |
|
||||
3 |
5074 |
45111 |
245633 |
1085609 |
|
||||
Mean |
5074 |
41385 |
230142 |
1028084 |
|
||||
6.25 |
1 |
5074 |
37275 |
206675 |
1019508 |
|
|||
2 |
5074 |
39510 |
231689 |
1063891 |
|
||||
3 |
5074 |
44180 |
207352 |
1116805 |
|
||||
Mean |
5074 |
40322 |
215239 |
1066735 |
|
||||
Control |
1 |
5074 |
36935 |
229684 |
1390325 |
|
|||
2 |
5074 |
38792 |
232968 |
1149068 |
|
||||
3 |
5074 |
38965 |
218495 |
1205538 |
|
||||
4 |
5074 |
34754 |
207573 |
1018664 |
|
||||
5 |
5074 |
40760 |
238934 |
1036277 |
|
||||
6 |
5074 |
39965 |
252976 |
1253996 |
|
||||
Mean |
5074 |
38362 |
230105 |
1175645 |
|
Evaluation after 72 h
Statistically significant differences of growth rates and yield compared to
control values are marked (+), not significant differences are marked (-).
Nominal test item concentration |
Replicate |
Growth rate |
Rate-related inhibition |
Yield |
Inhibition of yield |
||
[mg/L] |
No. |
[d-1] |
[%] |
[cells/mL] |
[%] |
||
100 |
1 |
1.73 |
4.81 |
894792 |
23.6 |
||
2 |
1.74 |
3.79 |
945735 |
19.2 |
|||
3 |
1.73 |
4.41 |
914509 |
21.9 |
|||
Mean |
(+)# |
1.74 |
4.34 |
(+) |
918345 |
21.6 |
|
100 |
1 |
-0.096 |
100 |
-1274 |
100 |
||
2 |
-0.065 |
100 |
-894 |
100 |
|||
3 |
-0.096 |
100 |
-1274 |
100 |
|||
Mean |
(+) |
-0.086 |
100 |
(+) |
-1147 |
100 |
|
50.0 |
1 |
-0.036 |
100 |
-514 |
100 |
||
2 |
-0.131 |
100 |
-1654 |
100 |
|||
3 |
-0.131 |
100 |
-1654 |
100 |
|||
Mean |
(+) |
-0.100 |
100 |
(+) |
-1274 |
100 |
|
25.0 |
1 |
1.69 |
6.89 |
798438 |
31.8 |
||
2 |
1.71 |
5.75 |
849971 |
27.4 |
|||
3 |
1.74 |
4.05 |
932471 |
20.3 |
|||
Mean |
(+)# |
1.71 |
5.56 |
(+) |
860293 |
26.5 |
|
12.5 |
1 |
1.75 |
3.79 |
946161 |
19.2 |
||
2 |
1.78 |
2.02 |
1042335 |
11.0 |
|||
3 |
1.79 |
1.36 |
1080535 |
7.69 |
|||
Mean |
(-) |
1.77 |
2.39 |
(-)* |
1023010 |
12.6 |
|
6.25 |
1 |
1.79 |
2.51 |
1014434 |
13.3 |
||
2 |
1.78 |
1.73 |
1058817 |
9.55 |
|||
3 |
1.80 |
0.84 |
1111731 |
5.03 |
|||
Mean |
(-) |
1.78 |
1.69 |
(-) |
1061661 |
9.31 |
|
Control |
1 |
1.87 |
1385251 |
||||
2 |
1.81 |
1143994 |
|||||
3 |
1.82 |
1200464 |
|||||
4 |
1.77 |
1013590 |
|||||
5 |
1.77 |
1031203 |
|||||
6 |
1.84 |
1248922 |
|||||
Mean |
1.81 |
1170571 |
Section-by-Section and Average
Specific Growth Rates of the Control Group
Replicate No. |
Specific growth rate [d-1] |
Mean (0 - 72 h) |
SD ± |
CV |
Mean CV [%] |
|||
section-by-section |
||||||||
0 - 24 h |
24 - 48 h |
48 - 72 h |
||||||
Control |
1 |
1.99 |
1.83 |
1.80 |
1.87 |
0.100 |
5.32 |
11.2 |
2 |
2.03 |
1.79 |
1.60 |
1.81 |
0.220 |
12.1 |
||
3 |
2.04 |
1.72 |
1.71 |
1.82 |
0.186 |
10.2 |
||
4 |
1.92 |
1.79 |
1.59 |
1.77 |
0.168 |
9.48 |
||
5 |
2.08 |
1.77 |
1.47 |
1.77 |
0.308 |
17.4 |
||
6 |
2.06 |
1.85 |
1.60 |
1.84 |
0.232 |
12.6 |
||
Mean |
1.81 |
|
||||||
SD ± |
0.04 |
|
||||||
CV [%] |
2.17 |
|
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- In this study LZ5593 was found to inhibit the growth of the freshwater green alga Desmodesmus subspicatus after 72 h. The NOEC-values for inhibition of specific growth rate and inhibition of yield after 72 h were 25.0 and 6.25 mg/L, respectively. The LOEC-values for inhibition of specific growth rate and inhibition of yield after 72 h were 50.0 and 12.5 mg/L, respectively. The EC50-values for inhibition of specific growth rate (ErC50) and yield (EyC50) after 72 h were 33.0 (31.7 – 34.2) and 28.5 (27.2 – 29.8) mg/L, respectively.
All effect levels are given based on nominal concentrations of LZ5593. - Executive summary:
The toxicity of LZ5593 to the unicellular freshwater green alga Desmodesmus subspicatus was determined according to the principles of OECD 201 from March 15 to 18, 2010. The aim of the study was to assess the effects on growth rate and yield over a period of 72 h.
The study was conducted under static conditions with an initial cell density of approximately 2 – 5 x 103cells/mL. Based on a preliminary test 5 concentration levels were tested in a geometrical series with a dilution factor of 2, nominal: 6.25 - 12.5 - 25.0 - 50.0 - 100 mg/L. Three replicates were tested for each test item concentration and six replicates for the control. Environmental conditions were determined to be within the acceptable limits.
The concentrations of LZ5593 were analysed at all concentration levels after 0 and 72 h via UV-spectrophotometry. The recovery rates related to the initial measured concentrations of the component sulphate were calculated to be in the range of 90 to 102 % in the concentration levels of 12.5 mg/L to 100 mg/L (6.25 mg/L: 125 %), demonstrating the stability of the test solutions throughout exposure. All effect values are given based on nominal concentrations of the test item.
NOEC, LOEC and EC - values of LZ5593(0-72 h)
based on nominal test item concentrations [mg/L]
Rate-related Inhibition
NOEC
25.0
LOEC
50.0
ErC10
26.9 (26.0 – 28.1)
ErC20
29.1 (28.1 – 30.4)
ErC50
33.0 (31.7 – 34.2)
Inhibition of Yield
NOEC
6.25
LOEC
12.5
EyC10
6.25
EyC20
23.5 (22.2 – 24.7)
EyC50
28.5 (27.2 – 29.8)
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