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EC number: 946-103-2 | CAS number: -
- 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
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2014-04-01 to 2014-03-31
- Reliability:
- 1 (reliable without restriction)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: The water accommodated fraction (WAF) was prepared with a nominal loading of the test item of 100 mg/L.
- Sampling method: The concentrations of the test item were analytically determined from the limit loading, the pH-control and the control after 0 hours (test start) and 72 hours (test end) via photometric analysis. Samples at test start were taken from an additional replicate without algae. At the end of the test samples were taken from pooled replicate with algae.
- Sample storage: All original samples were stored in a refrigerator until sample preparation. Prepared samples were stored at room temperature until analysis. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The water accommodated fraction (WAF) was prepared with a nominal loading of the test item of 100 mg/L.
100 mg/L of the test item were weighed out and transferred with an appropriate amount of dilution water into a brown glass flask. This dispersion was shaken for 24 hours with 20 rpm at room temperature. After a separation phase of 1 hour, the aqueous phase or WAF was removed by siphoning (from the approximate centre of the glass flask) to give the 100 mg/L loading rate WAF.
- Eluate: Dilution water
- Differential loading: None, limit test
- Controls: Six replicates (without test item) were tested under the same test conditions as the test vessels.
- pH-Controls: Six replicates, neutralized to pH 8.1 ± 0.2 with NaOH/HCl - 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): 4 days
- Method of cultivation: Fresh stocks were prepared every month on Z-Agar. Light intensity amounted to 35 - 70 µE x m-2 x s-1 for 24 h per day. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Post exposure observation period:
- No
- Hardness:
- not specified
- Test temperature:
- min.: 22.0 max.: 23.0, mean value: 22.5 °C
- pH:
- Nominal test item loading pH-value
[mg/L] Start; 0 hours End; 72 hours
100 10.58 8.38
100, pH-control 8.13 8.48
Control 8.18 8.52 - Dissolved oxygen:
- Not measured
- Salinity:
- Not measured, freshwater conditions
- Nominal and measured concentrations:
- See window "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, cotton wool plugs
- 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: Nominal: approximately 2 - 5 x 10^3 cells/mL, Actual: mean 4998 cells/mL
- Control end cells density: Mean 920143 cells/mL
- No. of vessels per concentration (replicates): 6
- No. of vessels per control (replicates): 6
- No. of vessels per pH-control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water:
Composition of Dilution Water
according to the guideline
Component Concentration [mg/L]
NH4Cl 15
MgCl2 x 6 H2O 12
CaCl2 x 2 H2O 18
MgSO4 x 7 H2O 15
KH2PO4 1.6
FeCl3 x 6 H2O 0.064
Na2EDTA x 2 H2O 0.1
H3BO3 0.185
MnCl2 x 4 H2O 0.415
ZnCl2 3 x 10^-3
Na2MoO4 x 2 H2O 7 x 10^-3
CoCl2 x 6 H2O 1.5 x 10^-3
CuCl2 x 2 H2O 1 x 10^-5
NaHCO3 50
pH 8.1 ± 0.2
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: yes, 8.1 ± 0.2 for pH-control samples
- Photoperiod: 24 h
- Light intensity and quality: 4440 - 8880 lux, corresponding to 60 - 120 µE x m^-2 x s^-1, mean value: 5225 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: [counting chamber; electronic particle counter; fluorimeter; spectrophotometer; colorimeter] fluorimeter, Cell density and self fluorescence was measured daily via Chlorophyll-a- fluorescence, excitation at 436 nm, emission at 685 nm. Dilution water was used as background signal.
TEST CONCENTRATIONS
Results of the Range Finding Test (0 - 72 hours)
Nominal Test Item Loading
[mg/L] Growth Rate Inhibition [%] Yield Inhibition [%]
100 (pH adjusted) 0 1
100 2 12
10 4 20
1 6 27 - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- < 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 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
- Effect concentrations exceeding solubility of substance in test medium: No - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
Current Study Valid Range (average ± 3 x SD)
Growth Rate Inhibition
ErC50 0.684 0.684 ± 0.281
95 % confidence interval 0.657 - 0.714 0.684 ± 0.281
Yield Inhibition
EyC50 0.315 0.314 ± 0.087
95 % confidence interval 0.297 - 0.3355 0.314 ± 0.087
SD = Standard deviation - Reported statistics and error estimates:
- NOEL/LOEL were determined by calculation of statistical significance of growth rate and yield. As standard One Way Analysis of Variance (ANOVA) and DUNNETT’s test were used for NOEL/LOEl calculations. When running a One Way Analysis of Variance a Normality test and an Equal Variance test were done first. The SHAPIRO-WILK-Test was used to test for normally distributed populations. The Levene median test was used for equal variance. P-values for both Normality and Equal Variance tests are 0.05. The alpha-value (acceptable probability of incorrectly concluding that there is a difference) is alpha=0.05.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In this study celitement was found slightly to inhibit the growth rate of the freshwater green alga Desmodesmus subspicatus after 72 hours. The NOEC-value of the test item for both, inhibition of growth rate and inhibition of yield, after 72 hours was < 100 mg/L. The EC50-values of the test item for inhibition of growth rate (ErC50) and yield (EyC50) after 72 hours were both > 100 mg/L, respectively.
All effect levels are given based on the nominal concentration of celitement. - Executive summary:
The toxicity of celitement to the unicellular freshwater green alga Desmodesmus subspicatuswas determined according to the principles of OECD 201 (2011) at Dr.U.Noack-Laboratorien in 31157 Sarstedt, Germany from2014-03-31 to 2014-04-04 with the definitive exposure phase from 2014-04-01 to 2014-04-04. The aim of the study was to assess the effects on growth rate and yield over a period of 72 hours.
The test item is a mixture, solid and insoluble in water. In view of the difficulties associated with the evaluation of aquatic toxicity of complex mixture test items, a modification of the standard method for the preparation of aqueous media was performed. An approach endorsed by several important regulatory authorities in the EU and elsewhere (ECETOC 1996 and OECD 2000), is to expose the organisms to a Water Accommodated Fraction (WAF*) of the test item in cases where the test item is a complex mixture. Exposures are expressed in terms of the original concentration of the test item in water at the start of the mixing period (loading rate) irrespective of the actual concentration of the test item in the WAF.
The study was conducted under static conditions with an initial cell density of 4998 cells/mL. One limit loading of 100 mg/L of the test item was prepared. The test item was applied onto a glass slide. The glass slide with the test item was inserted in a brown glass flask with an appropriate amount of dilution water. This dispersion was shaken for 24 hours with 20 rpm at room temperature.After a separation phase of 1 hour,the aqueous phase or WAF was removed by siphoning (from the approximate centre of the glass flask) to give the 100 mg/L loading rate WAF. The water soluble fraction was clear. Six replicates were tested for the limit loading, the pH - neutralized limit loading (pH – control) and for the control. Environmental conditions were within the acceptable limits.
The concentrations of the test item celitement were analytically evaluated via photometric analysis of silicon at the start of the exposure (0 h) and at the end of the exposure (72 h) of the limit loading level, the pH-control and the control.
The measured silicon concentration at the start of the exposure (0 h) was 7.45 mg/L in the limit loading level and 7.65 mg/L in the pH-control. At the end of the exposure the measured silicon concentrations gave recoveries of 98 and 102 % of the initially measured values of the limit loading and the pH-control indicating the stability of the test item in the WAF during the exposure phase.All effect values given are based on the nominal test item loading of celitement.
* Water accommodated fractions (WAF): The aqueous medium containing only the fraction of a multi-component test item that is dissolved and / or present as a stable dispersion/emulsion under test conditions in the test medium, acc. to OECD Guidance Document, No. 23.
Reference
Cell Densities
Nominal Test Item Loading |
Replicate |
Cell Density [cells/mL] |
|||
[mg/L] |
No. |
0 hours |
24 hours |
48 hours |
72 hours |
100 |
1 |
4998 |
26587 |
164666 |
719393 |
2 |
4998 |
21181 |
150745 |
639043 |
|
3 |
4998 |
22970 |
139301 |
641815 |
|
4 |
4998 |
22216 |
148224 |
637571 |
|
5 |
4998 |
20730 |
151057 |
664642 |
|
6 |
4998 |
22155 |
167170 |
665162 |
|
Mean |
4998 |
22640 |
153527 |
661271 |
|
100 neutralized (pH-control) |
1 |
4998 |
37017 |
193159 |
884813 |
2 |
4998 |
30164 |
192154 |
774316 |
|
3 |
4998 |
35964 |
194865 |
727233 |
|
4 |
4998 |
31741 |
166321 |
756947 |
|
5 |
4998 |
34704 |
200713 |
729009 |
|
6 |
4998 |
30017 |
183075 |
681839 |
|
Mean |
4998 |
33268 |
188381 |
759026 |
|
Control |
1 |
4998 |
37229 |
182304 |
908159 |
2 |
4998 |
30654 |
199552 |
835217 |
|
3 |
4998 |
27877 |
221097 |
976857 |
|
4 |
4998 |
29211 |
200427 |
931636 |
|
5 |
4998 |
27812 |
191530 |
883470 |
|
6 |
4998 |
32638 |
205495 |
985520 |
|
Mean |
4998 |
30904 |
200068 |
920143 |
Evaluation after 72 hours
Statistically significant differences of growth rates and yield compared to
control values are marked (+), not significant differences are marked (-).
Nominal Test Item Loading |
Replicate |
Growth Rate |
Growth Rate Inhibition |
Yield |
Yield Inhibition |
||
[mg/L] |
No. |
[d-1] |
[%] |
[cells/mL] |
[%] |
||
100 |
1 |
|
1.66 |
5 |
|
714395 |
22 |
2 |
|
1.62 |
7 |
|
634045 |
31 |
|
3 |
|
1.62 |
7 |
|
636817 |
30 |
|
4 |
|
1.62 |
7 |
|
632573 |
31 |
|
5 |
|
1.63 |
6 |
|
659644 |
28 |
|
6 |
|
1.63 |
6 |
|
660164 |
28 |
|
Mean |
(+) |
1.63 |
6 |
(+) |
656273 |
28 |
|
100 neutralized (pH-control) |
1 |
|
1.73 |
1 |
|
879815 |
4 |
2 |
|
1.68 |
3 |
|
769318 |
16 |
|
3 |
|
1.66 |
4 |
|
722235 |
21 |
|
4 |
|
1.67 |
4 |
|
751949 |
18 |
|
5 |
|
1.66 |
4 |
|
724011 |
21 |
|
6 |
|
1.64 |
6 |
|
676841 |
26 |
|
Mean |
(+) |
1.67 |
4 |
(+) |
754028 |
18 |
|
Control |
1 |
|
1.73 |
|
|
903161 |
|
2 |
|
1.71 |
|
|
830219 |
|
|
3 |
|
1.76 |
|
|
971859 |
|
|
4 |
|
1.74 |
|
|
926638 |
|
|
5 |
|
1.73 |
|
|
878472 |
|
|
6 |
|
1.76 |
|
|
980522 |
|
|
Mean |
|
1.74 |
|
|
915145 |
|
Section-by-Section and Average
Specific Growth Rates of the Control Group
(0 – 72 hours)
|
Replicate No. |
Specific Growth Rate [d-1] |
Mean (0 - 72 h) |
SD ± |
CV |
Mean CV [%] |
||
Section-by-Section |
||||||||
0 - 24 hours |
24 - 48 hours |
48 - 72 hours |
||||||
Control |
1 |
2.01 |
1.59 |
1.61 |
1.73 |
0.237 |
13.7 |
12.8 |
2 |
1.81 |
1.87 |
1.43 |
1.71 |
0.240 |
14.0 |
||
3 |
1.72 |
2.07 |
1.49 |
1.76 |
0.295 |
16.8 |
||
4 |
1.77 |
1.93 |
1.54 |
1.74 |
0.196 |
11.2 |
||
5 |
1.72 |
1.93 |
1.53 |
1.73 |
0.201 |
11.6 |
||
6 |
1.88 |
1.84 |
1.57 |
1.76 |
0.169 |
9.58 |
||
|
|
|
Mean |
1.74 |
|
|
||
|
|
|
SD ± |
0.02 |
|
|||
|
|
|
CV [%] |
1.20 |
|
Description of key information
Short-term toxicity testing with the freshwater green alga Desmodesmus subspicatus was carried out according to the OECD 201 guidance taking into account GLP and thus resulting in a Klimish 1 score. No acute toxicity was observed.
Key value for chemical safety assessment
Additional information
The NOEC-value of the test item for both, inhibition of growth rate and inhibition of yield, after 72 hours was < 100 mg/L. The EC50-values of the test item for inhibition of growth rate (ErC50) and yield (EyC50) after 72 hours were both > 100 mg/L, respectively.
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