Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
Reaction mass of 3,4,5-trichlorophthalic acid, strontium salt and 3,4,6-trichlorophthalic acid, strontium salt and 3,4-dichlorophthalic acid, strontium salt and 3,5-dichlorophthalic acid, strontium salt and 3,6-dichlorophthalic acid, strontium salt and 3-chlorophthalic acid, strontium salt and 4,5-dichlorophthalic acid, strontium salt and 4-chlorophthalic acid, strontium salt
EC number: 925-568-5 | 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:
- 2019-09-17 to 2019-11-13
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- adopted March 2006, corrected July 28, 2011, equivalent to Commission Regulation (EC) NO 761/2009
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Filtrate of 100 mg test item/L representing the highest test concentration and dilutions of 1:3.125, 1:10, 1:31.25 and 1:100 of this filtrate was tested
- Sampling method: The samples were taken from the biological phase of the study. Duplicate samples from the freshly prepared test media (containing algae) of all test concentrations and from the control were taken at the start of the test. For the determination of the stability of the test item under the test conditions and of the maintenance of the test item concentrations during the test period, duplicate samples from the test media of all test concentrations and the control (containing algae) were taken at the end of the test (after the 72 hours test period) by pouring together the contents of the test beakers of each treatment.
- Sample storage conditions before analysis: All samples from test start were stored in a freezer (≤ - 20 °C), protected from light until analysis was performed, samples from test end were analyzed directly after sampling. Afterwards all samples were stored deep frozen (≤ -20 °C) and will be kept stored up to the date of the final report. - Vehicle:
- no
- Details on test solutions:
- The test medium of the highest test concentration of nominal 100 mg test item/L was prepared by dissolving 100.6 mg test item into 1006 mL test water by intense stirring for 25 minutes and ultrasonic treatment for 5 minutes. Adequate volumes of this test medium were diluted with test water to prepare the test media of the other desired test concentrations.
The test media were prepared just before introduction of the algae (= start of the test).
-Eluate: N/A
-Differential loading: N/A
-Controls: In the control, test water was used without addition of the test item
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): No vehicle used
- Concentration of vehicle in test medium (stock solution and final test solution(s) or suspension(s) including control(s): N/A
- Evidence of undissolved material (e.g. precipitation, surface film, ect.): There were no remarkable observations in the test medium. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- - Common name: Pseudokirchneriella subcapitata (KORSHIKOV) formerly known as Selenastrum capricornutum, and recently renamed as Raphidocelis subcapitata (KORSHIKOV)
- Strain: Strain No. 61.81 SAG
- Source (laboratory, culture collection): The algae were originally supplied by the „Sammlung von Algenkulturen, Albrecht-von-Haller-Institut für Pflanzenwissenschaften, Universität Göttingen (SAG)", 37073 Göttingen, Germany.
- Method of cultivation: The algae were cultivated in the laboratories of ibacon under standardized conditions according to the test guidelines.
Reference Item: For the evaluation of the quality of the algae and the experimental conditions the reference item potassium dichromate is tested at least twice a year to demonstrate satisfactory test conditions.
ACCLIMATION
- Acclimation period: N/A
- Culturing media and conditions (same as test or not): same as test.
- Any deformed or abnormal cells observed: No. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Hardness:
- 0.24 mmol/L (= 24 mg/L) as CaCO3
- Test temperature:
- The temperature was measured daily in an Erlenmeyer flask filled with water and incubated under the same conditions as the test flasks.
Water temperature: 21.4 to 22.0 °C - pH:
- The pH was measured in all test item concentrations and the control at the start and the end of the test.
pH value in the control at test start: 8.1 to 9.1 at test end. - Nominal and measured concentrations:
- At the start of the test 95 % of the nominal test concentrations were found (average of the nominal concentrations of 100, 32, 10 and 3.2 mg test item/L). After 72 hours test duration, 96 % of the nominal value was determined (average of the nominal concentrations of 100, 32, 10 and 3.2 mg test item/L). During the test the algae were exposed to a mean of 95 % of nominal.
- Details on test conditions:
- TEST SYSTEM
-Test vessel: Erlenmeyer flasks
-Type: open
-Material, size, headspace, fill volume: 50 mL volume with nominal 50 mL of test medium
-Aeration: No
- Type of flow-through (e.g. peristaltic or proportional diluter): No, static
- Renewal rate of test solution (frequency/flow rate): N/A
- Initial cells density: 5000 algal cells per mL test medium; These cells were taken from an exponentially growing pre-culture, which was set up 4 days prior to the test start under the same conditions as in the test.
- Control end cells density: 814 770 000 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates):6
- No. of vessels per vehicle control (replicates): N/A
The test was performed with three replicates per test concentration and six replicates in the control. Volumes of 50 mL of algal suspension per replicate were continuously stirred with magnetic stirrers in 50 mL Erlenmeyer flasks. The flasks were covered with glass stoppers and incubated in a water bath. The flasks were placed in a random order and were repositioned each day to minimize differences in test conditions.
Additionally, one replicate of each test concentration and of the control was prepared without algae to provide a "blank" for the spectrophotometric measurements. The additional replicates were incubated under the same conditions as described above. The blank values were subtracted from the absorption measured in the samples containing algae in order to eliminate absorption caused by the test item.
GROWTH MEDIUM
- Standard medium used: yes
- Detailed composition if non-standard medium was used: N/A
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Deionised water, Analytical grade salts were added to achieve OECD medium
- Culture medium different from test medium: No
- Intervals of water quality measurement: Start and end; Test conditions were recorded with suitable instruments and documented.
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: No
- Photoperiod: Continuous illumination
- Light intensity and quality: The light intensity was measured once during the test at 6 positions distributed over the experimental area at the surface of the test media.
Mean light intensity: 5034 lux (range: 4815 to 5190 lux)
- Salinity (for marine algae): N/A
EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
- Determination of cell concentrations: The cell density on each observation time was determined by spectrophotometric measurement. Therefore, defined volumes of the algal suspensions from all replicates and from the blanks were sampled after 24, 48 and 72 hours of exposure, and were not replaced. The algal cell densities were calculated by subtracting the absorption of the blanks, from each of the measured absorption of the test media (with algae).
Based on the counted cell densities and the absorption from an algal suspension and its dilutions, a linear regression was performed for the calculation of the cell densities of the replicates during the test.
- Chlorophyll measurement: No
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.16
- Justification for using less concentrations than requested by guideline: N/A
Range finding study
- Test concentrations: test medium of 100 mg/L and dilutions thereof of 1:3.126, 1:10 1:31.25 and 1:100 and a control
- Results used to determine the conditions for the definitive study: Yes
Pre-experiments were performed to determine a suitable concentration range and to establish suitable methods to prepare the test solutions. The pre-experiments were not performed in compliance with the GLP-Regulations and are excluded from the Statement of Compliance in the final report, but the raw data of these tests will be archived under the study number of the present study. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- not determinable because of methodological limitations
- Duration:
- 72 h
- Dose descriptor:
- EC20
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- not determinable because of methodological limitations
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- not determinable because of methodological limitations
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 32 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- 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): No. The microscopic examination of the shape of the algal cells after 72 hours of test duration did not show any difference between the algae that had been growing up to a nominal test concentration of 100 mg test item/L and the algal cells in the control. Thus, the shape of the algal cells was not obviously affected up to this test concentration, the highest concentration tested.
- Unusual cell shape: No
- Color differences: No
- Flocculation: No
- Adherence to test vessels: No
- Aggregation of algal cells: No
- Any stimulation of growth found in any treatment: 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
- ErC50: 0.941 mg test item/L (95 % C.I.: 0.910 - 0.973 mg test item/L) - Reported statistics and error estimates:
- Based on the calculated cell densities, the 72 hour ErC50 and the 72 hour EyC50, the corresponding EC20 and EC10 values and where possible their 95 %-confidence limits were calculated by Probit analysis.
For the determination of the 72 hour LOEC and the 72 hour NOEC, the calculated growth rates and yields at each test concentration were tested for significant differences compared to the control values by Williams Multiple Sequential t-test (yield and growth rate).
The software used to perform the statistical analysis was ToxRat Professional, Version 3.3.0, ToxRat Solutions GmbH. - Validity criteria fulfilled:
- yes
- Conclusions:
- The 72-hour EC50 for yield and growth rate were calculated to be > 100 mg test item/L. The 72-hour NOEC for yield and growth rate was determined to be 32 mg test item/L and the associated 72-hour LOEC for yield and growth rate was 100 mg test item/L. Growth inhibition at 100 mg/L was 2.5 % compared to the control group.
The initial concentrations and the maintenance of the exposure concentrations during the test were verified in the analytical part. All reported results refer to nominal values since the concentrations of the test item were within ± 20% of the nominal concentrations during the test. - Executive summary:
In a 72 hour acute toxicity study, the cultures of Pseudokirchneriella subcapitata (KORSHOKOV), Strain No. 61.81 were exposed to Strontium dichlorophthalate at nominal concentrations of 100, 32, 10, 3.2 and 1.0 mg test item/L under static or renewal conditions in accordance with the OECD guideline 201. The NOEC and EC50 values based on Yield and growth rate were 32 mg test item/L and <100 mg test item, respectively. The % yield inhibition in the treated algal culture as compared to the control ranged from -4.2 % in the lowest treatment concentration to 11.8% in the highest tested concentration after 72 hours, and the % growth inhibition in the treated groups compared to the control group ranged from -0.8 to 2.5 %, respectively.
This toxicity study is classified as acceptable and satisfies the guideline requirements for Freshwater alga and Cyanobacteria, Growth Inhibition test with P. subcapitata.
Results Synopsis
Test Organism: of Pseudokirchneriella subcapitata (KORSHIKOV), Strain No. 61.81 SAG
Test Type (Flowthrough, Static, Static Renewal): Static
Parameter
Yield
[mg test item/L]Growth rate
[mg test item/L]72-hour EC50
>100
>100
95 % conf. interval
n.d.
n.d.
72-hour EC20
>100
>100
95 % conf. interval
n.d.
n.d.
72-hour EC10
>100
>100
95 % conf. interval
n.d.
n.d.
72-hour NOEC
32
32
72-hour LOEC
100
100
n.d. = not determinable
Endpoint(s) Effected: Growth rate, Yield
Reference
Biological results:
The 72-hour EC50 for yield and growth rate was calculated to be >100 mg test item/L. The 72-hour EyC10was calculated to be > 100 mg test item/L and the ErC10> 100 mg test item/L. The 72-hour NOEyC was determined to be 32 mg test item/L and the associated 72-hour LOEyC of 100 mg test item/L. The 72-hour NOErC was determined to be 32 mg test item/L and the associated 72-hour LOErC is 100 mg test item/L.
Table 1: Influence of Strontium Dichlorophthalate on the Growth of Pseudokirchneriella subcapitata. The reported results refer to nominal values since the concentrations of the test item were within ± 20% of the nominal concentrations during the test.
Parameter |
Yield |
Growth rate |
72-hour EC50 |
>100 |
>100 |
95 % conf. interval |
n.d. |
n.d. |
|
|
|
72-hour EC20 |
>100 |
>100 |
95 % conf. interval |
n.d. |
n.d. |
|
|
|
72-hour EC10 |
> 100 |
>100 |
95 % conf. interval |
n.d. |
n.d. |
|
|
|
72-hour NOEC |
32 |
32 |
72-hour LOEC |
100 |
100 |
n.d. = not determinable |
Analytical Results:
The quantification of the test item strontium dichlorophthalate in the test samples was performed using liquid chromatography with UV detection. At the start of the test 95 % of the nominal test concentrations were found (average of the nominal concentrations of 100, 32, 10 and 3.2 mg test item/L). After 72 hours test duration, 96 % of the nominal value was determined (average of the nominal concentrations of 100, 32, 10 and 3.2 mg test item/L). During the test the algae were exposed to a mean of 95 % of nominal.
Validity criteria of the test:
Cell Density |
|
Coefficient of Variation of Sectional (Daily) Growth Rates in Control Cultures: |
|
Coefficient of Variation of Average Growth between Control Replicates: |
|
Table 2: Algal Cell Densities during the Test Period of 72 Hours
Nominal concentration [mg test item/L] |
Flask no. |
Density of algal cells [10000/mL] after |
|||
24 hours |
48 hours |
72 hours |
|||
Control |
1 |
2.709 |
18.192 |
81.795 |
|
2 |
2.709 |
19.145 |
79.889 |
||
3 |
3.185 |
19.860 |
83.224 |
||
4 |
2.947 |
18.192 |
81.795 |
||
5 |
2.947 |
19.384 |
79.651 |
||
6 |
3.185 |
18.192 |
82.510 |
||
m |
2.947 |
18.828 |
81.477 |
||
s |
0.213 |
0.733 |
1.427 |
||
1.0 |
1 |
2.709 |
20.098 |
84.892 |
|
2 |
3.185 |
20.813 |
83.701 |
||
3 |
3.185 |
18.192 |
86.083 |
||
m |
3.026 |
19.701 |
84.892 |
||
s |
0.275 |
1.355 |
1.191 |
||
3.2 |
1 |
2.470 |
16.763 |
79.651 |
|
2 |
2.709 |
18.907 |
83.939 |
||
3 |
2.709 |
18.431 |
80.604 |
||
m |
2.629 |
18.034 |
81.398 |
||
s |
0.138 |
1.126 |
2.251 |
||
10 |
1 |
3.185 |
20.336 |
89.656 |
|
2 |
2.947 |
20.575 |
85.606 |
||
3 |
2.947 |
19.384 |
77.031 |
||
m |
3.026 |
20.098 |
84.098 |
||
s |
0.138 |
0.630 |
6.446 |
||
32 |
1 |
3.185 |
19.860 |
82.510 |
|
2 |
2.709 |
19.145 |
81.080 |
||
3 |
2.709 |
18.669 |
74.887 |
||
m |
2.867 |
19.225 |
79.492 |
||
s |
0.275 |
0.599 |
4.052 |
||
100 |
1 |
2.709 |
16.763 |
70.123 |
|
2 |
2.470 |
14.143 |
75.840 |
||
3 |
2.470 |
15.810 |
69.884 |
||
m |
2.550 |
15.572 |
71.949 |
||
s |
0.138 |
1.326 |
3.372 |
||
m: mean value; s: standard deviation |
|||||
Table 3: Yield during the test period of 72 hours
Nominal concentration [mg test item/L] |
Flask no. |
Yield Y [10000 cells/mL] after |
||
24 hours |
48 hours |
72 hours |
||
Control |
1 |
2.209 |
17.692 |
81.295 |
2 |
2.209 |
18.645 |
79.389 |
|
3 |
2.685 |
19.360 |
82.724 |
|
4 |
2.447 |
17.692 |
81.295 |
|
5 |
2.447 |
18.884 |
79.151 |
|
6 |
2.685 |
17.692 |
82.010 |
|
m |
2.447 |
18.328 |
80.977 |
|
s |
0.213 |
0.733 |
1.427 |
|
1.0 |
1 |
2.209 |
19.598 |
84.392 |
2 |
2.685 |
20.313 |
83.201 |
|
3 |
2.685 |
17.692 |
85.583 |
|
m |
2.526 |
19.201 |
84.392 |
|
s |
0.275 |
1.355 |
1.191 |
|
3.2 |
1 |
1.970 |
16.263 |
79.151 |
2 |
2.209 |
18.407 |
83.439 |
|
3 |
2.209 |
17.931 |
80.104 |
|
m |
2.129 |
17.534 |
80.898 |
|
s |
0.138 |
1.126 |
2.251 |
|
10 |
1 |
2.685 |
19.836 |
89.156 |
2 |
2.447 |
20.075 |
85.106 |
|
3 |
2.447 |
18.884 |
76.531 |
|
m |
2.526 |
19.598 |
83.598 |
|
s |
0.138 |
0.630 |
6.446 |
|
32 |
1 |
2.685 |
19.360 |
82.010 |
2 |
2.209 |
18.645 |
80.580 |
|
3 |
2.209 |
18.169 |
74.387 |
|
m |
2.367 |
18.725 |
78.992 |
|
s |
0.275 |
0.599 |
4.052 |
|
100 |
1 |
2.209 |
16.263 |
69.623 |
2 |
1.970 |
13.643 |
75.340 |
|
3 |
1.970 |
15.310 |
69.384 |
|
m |
2.050 |
15.072 |
71.449 |
|
m: mean value; s: standard deviation |
Table 4: Growth rate during the Test Period of 72 Hours
Nominal concentration [mg test item/L] |
Flask no. |
Growth rates [µ/day] after |
||
0 - 24 hours |
0 - 48 hours |
0 - 72 hours |
||
Control |
1 |
1.690 |
1.797 |
1.699 |
2 |
1.690 |
1.823 |
1.691 |
|
3 |
1.852 |
1.841 |
1.705 |
|
4 |
1.774 |
1.797 |
1.699 |
|
5 |
1.774 |
1.829 |
1.690 |
|
6 |
1.852 |
1.797 |
1.702 |
|
m |
1.772 |
1.814 |
1.698 |
|
s |
0.072 |
0.019 |
0.006 |
|
1.0 |
1 |
1.690 |
1.847 |
1.712 |
2 |
1.852 |
1.864 |
1.707 |
|
3 |
1.852 |
1.797 |
1.716 |
|
m |
1.798 |
1.836 |
1.711 |
|
s |
0.094 |
0.035 |
0.005 |
|
3.2 |
1 |
1.598 |
1.756 |
1.690 |
2 |
1.690 |
1.816 |
1.708 |
|
3 |
1.690 |
1.804 |
1.694 |
|
m |
1.659 |
1.792 |
1.697 |
|
s |
0.053 |
0.032 |
0.009 |
|
10 |
1 |
1.852 |
1.853 |
1.730 |
2 |
1.774 |
1.859 |
1.714 |
|
3 |
1.774 |
1.829 |
1.679 |
|
m |
1.800 |
1.847 |
1.708 |
|
s |
0.045 |
0.016 |
0.026 |
|
32 |
1 |
1.852 |
1.841 |
1.702 |
2 |
1.690 |
1.823 |
1.696 |
|
3 |
1.690 |
1.810 |
1.670 |
|
m |
1.744 |
1.825 |
1.689 |
|
s |
0.094 |
0.016 |
0.017 |
|
100 |
1 |
1.690 |
1.756 |
1.648 |
2 |
1.598 |
1.671 |
1.674 |
|
3 |
1.598 |
1.727 |
1.647 |
|
m |
1.628 |
1.718 |
1.656 |
|
s |
0.053 |
0.043 |
0.015 |
|
m: mean value; s: standard deviation |
Table 5: Yield y and Percentage Inhibition of y during the Test Period
Nominal concentration [mg test item/L] |
Yields y [10000 cells/mL] and % inhibition of y during the test period |
|||||
0 - 24 hours |
0-48 hours |
0-72 hours |
||||
y |
% |
y |
% |
y |
% |
|
Control |
2.447 |
- |
18.328 |
- |
80.977 |
- |
1.0 |
2.526 |
-3.2 |
19.201 |
-4.8 |
84.392 |
-4.2 |
3.2 |
2.129 |
13.0 |
17.534 |
4.3 |
80.898 |
0.1 |
10 |
2.526 |
-3.2 |
19.598 |
-6.9 |
83.598 |
-3.2 |
32 |
2.367 |
3.2 |
18.725 |
-2.2 |
78.992 |
2.5 |
100 |
2.050 |
16.2* |
15.072 |
17.8* |
71.449 |
11.8* |
negative values in ‘% inhibition’ indicate an increase in growth relative to that of the control * mean value significantly different from the control (tested with Williams Multiple Sequential t-test (24, 48 and 72h),α= 0.05, one-sided smaller) |
Table 6: Growth Rates µ and Percentage Inhibition of µ during the Test Period
Nominal concentration [mg test item/L] |
Growth rates µ [1/day] and % inhibition of µ during the test period |
|||||
0 - 24 hours |
0-48 hours |
0-72 hours |
||||
µ |
% |
µ |
% |
µ |
% |
|
Control |
1.772 |
- |
1.814 |
- |
1.698 |
- |
1.0 |
1.798 |
-1.5 |
1.836 |
-1.2 |
1.711 |
-0.8 |
3.2 |
1.659 |
6.4 |
1.792 |
1.2 |
1.697 |
0.0 |
10 |
1.800 |
-1.6 |
1.847 |
-1.8 |
1.708 |
-0.6 |
32 |
1.744 |
1.6 |
1.825 |
-0.6 |
1.689 |
0.5 |
100 |
1.628 |
8.1* |
1.718 |
5.3* |
1.656 |
2.5* |
negative values in ‘% inhibition’ indicate an increase in growth relative to that of the control
* mean value significantly different from the control (tested with Williams Multiple Sequential t-test (24, 48 and 72h), α = 0.05, one-sided smaller)
Table 7: Summary of Analytical Results
Sample description [mg test item/mL] |
% of nominal1 |
RSD [%] |
n |
Control |
n.a. |
n.a. |
4 |
3.2 |
92 |
2 |
4 |
10 |
96 |
2 |
4 |
32 |
97 |
1 |
4 |
100 |
98 |
1 |
4 |
1mean value of all measured samples per treatment group
RSD: relative standard deviation per treatment group
n: number of analysed samples; n.a.: not applicable
Description of key information
Strontium dichlorophthalate was tested on the freshwater algae Pseudokirchneriella subcapitata according to OECD guideline No. 201. The tested concentrations were 100, 32, 10, 3.2 and 1.0 mg test item/L, and a control. The result of the study was a EC50 of > 100 mg test item/L and a NOEC of 32 mg test item/L based on the growth rate.
Key value for chemical safety assessment
- EC10 or NOEC for freshwater algae:
- 32 mg/L
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
