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EC number: 940-307-5 | 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:
- June 03 - July 25, 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- The concentrations of the test item were determined in fresh media (0 hours) and at the end of the exposure interval (72 hours) via HPLC - DAD.
- Vehicle:
- yes
- Remarks:
- water
- Details on test solutions:
- A saturated solution with a nominal loading of 100 mg test item/L was prepared once 24 ± 1 hour prior to the start of the exposure. An appropriate amount of the test item was weighed out. The test
item was applied onto a glass slide. The glass slide with the test item was inserted into a brown glass bottle with an appropriate amount of dilution water. The saturated solution was
stirred for 24 ± 1 hours (1100 rpm, room temperature) with a magnetic stirrer. After a separation phase of 1 hour the saturated solution was removed by siphoning from the middle of the flask.
Undissolved particles were removed by membrane filtration (membrane filter 0.45 μm, RC, Macherey-Nagel). The filter was saturated in order to avoid adsorption during the filtration. The first
25 ml of the filtrate were discarded. The filtration was interrupted for 15 minutes to allow adsorption and saturation of the filter material with dissolved test item. Thereafter, the filtration was
continued. The next 25 ml were discarded. The following test item solution was used in the test. During filtration, the filter was always kept covered. The saturated solution was checked via laser beam
(Tyndall effect) for undissolved test item. The Tyndall effect was negative. - Test organisms (species):
- Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- Test organism: Pseudokirchneriella subcapitata HINDAK, CCAP 278/4
Origin:
Sammlung von Algenkulturen (SAG), Pflanzenphysiologisches Institut der Universität Göttingen, Göttingen, Germany - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Details on test conditions:
- The study was performed as a static test in open vessels under culture conditions. The flasks contained 100 mL either reconstituted water or test medium (test item group).
The duration of exposure was 72 hours. The algal biomass in each flask was determined daily during the exposure period via Chlorophyll a-fluorescence excitation at 436, emission at 685 nm.
Microscopic evaluation of the cells at the start and at the end of the incubation period was carried out. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 363 µg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 85 µg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 20 µg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- The EC50-values with confidence interval for inhibition of growth rate (ErC50) and yield (EyC50) after 72 hours were 363 (314 – 425) µg/L and 97.1 (74.5 - 128) µg/L.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The EC50-values with confidence interval for inhibition of growth rate (ErC50) was 363 (314 – 425) µg/L. The EC10-values with confidence interval for inhibition of growth rate (ErC10) was 85.0 (57.7 – 113) µg/L.
- Executive summary:
The information for this endpoint study record was obtained from an experimental study. The OECD GLP criteria were met and the methods applied are fully compliant with OECD TG 201. The EC50-values with confidence interval for inhibition of growth rate (ErC50) was 363 (314 – 425) µg/L. The EC10-values with confidence interval for inhibition of growth rate (ErC10) was 85.0 (57.7 – 113) µg/L.
Reference
1) Cell Densities
Initial measured test item concentration |
Replicate |
Cell density [cells/mL] |
|||
[µg/L] |
No. |
0 hours |
24 hours |
48 hours |
72 hours |
634 |
1 |
5416 |
7981 |
7882 |
6589 |
2 |
5416 |
8059 |
9583 |
9159 |
|
3 |
5416 |
7716 |
9004 |
9035 |
|
Mean |
5416 |
7919 |
8823 |
8261 |
|
207 |
1 |
5416 |
10815 |
49768 |
269641 |
2 |
5416 |
10036 |
52475 |
290525 |
|
3 |
5416 |
11791 |
64402 |
449855 |
|
Mean |
5416 |
10881 |
55548 |
336674 |
|
61.2 |
1 |
5416 |
12837 |
106695 |
833550 |
2 |
5416 |
12966 |
99948 |
769536 |
|
3 |
5416 |
17825 |
142192 |
1152210 |
|
Mean |
5416 |
14543 |
116278 |
918432 |
|
20.0 |
1 |
5416 |
17389 |
154752 |
1241805 |
2 |
5416 |
19285 |
173717 |
1313900 |
|
3 |
5416 |
17596 |
169219 |
1256166 |
|
Mean |
5416 |
18090 |
165896 |
1270624 |
|
6.34 |
1 |
5416 |
18859 |
170514 |
1399942 |
2 |
5416 |
17391 |
122925 |
1096057 |
|
3 |
5416 |
19470 |
169979 |
1330573 |
|
Mean |
5416 |
18573 |
154473 |
1275524 |
|
2.00 |
1 |
5416 |
19957 |
159951 |
1338386 |
2 |
5416 |
18041 |
150370 |
1217076 |
|
3 |
5416 |
21434 |
168402 |
1497108 |
|
Mean |
5416 |
19811 |
159574 |
1350857 |
|
Control |
1 |
5416 |
19772 |
181613 |
1272936 |
2 |
5416 |
23700 |
188341 |
1535784 |
|
3 |
5416 |
20728 |
195049 |
1412526 |
|
4 |
5416 |
22262 |
189168 |
1477903 |
|
5 |
5416 |
20446 |
191223 |
1451762 |
|
6 |
5416 |
19370 |
176112 |
1352187 |
|
Mean |
5416 |
21046 |
186918 |
1417183 |
2) Evaluation after 72 hours
Statistically significant differences of growth rates and yield compared
to control values are marked (+), not significant differences are marked
(-).
Initial measured test item concentration |
Replicate |
Growth Rate |
Inhibition of Growth Rate |
Yield |
Inhibition of Yield |
||
[µg/L] |
No. |
[d-1] |
[%] |
[cells/mL] |
[%] |
||
634 |
1 |
|
0.0653 |
96 |
|
1173 |
100 |
2 |
|
0.175 |
91 |
|
3743 |
100 |
|
3 |
|
0.171 |
91 |
|
3619 |
100 |
|
Mean |
(+) |
0.137 |
93 |
(+) |
2845 |
100 |
|
207 |
1 |
|
1.30 |
30 |
|
264225 |
81 |
2 |
|
1.33 |
28 |
|
285109 |
80 |
|
3 |
|
1.47 |
21 |
|
444439 |
69 |
|
Mean |
(+) |
1.37 |
26 |
(+) |
331258 |
77 |
|
61.2 |
1 |
|
1.68 |
10 |
|
828134 |
41 |
2 |
|
1.65 |
11 |
|
764120 |
46 |
|
3 |
|
1.79 |
4 |
|
1146794 |
19 |
|
Mean |
(+) |
1.71 |
8 |
(+) |
913016 |
35 |
|
20.0 |
1 |
|
1.81 |
2 |
|
1236389 |
12 |
2 |
|
1.83 |
1 |
|
1308484 |
7 |
|
3 |
|
1.82 |
2 |
|
1250750 |
11 |
|
Mean |
(-) |
1.82 |
2 |
(-) |
1265208 |
10 |
|
6.34 |
1 |
|
1.85 |
0 |
|
1394526 |
1 |
2 |
|
1.77 |
5 |
|
1090641 |
23 |
|
3 |
|
1.84 |
1 |
|
1325157 |
6 |
|
Mean |
(-) |
1.82 |
2 |
(-) |
1270108 |
10 |
|
2.00 |
1 |
|
1.84 |
1 |
|
1332970 |
6 |
2 |
|
1.81 |
3 |
|
1211660 |
14 |
|
3 |
|
1.87 |
-1 |
|
1491692 |
-6 |
|
Mean |
(-) |
1.84 |
1 |
(-) |
1345441 |
5 |
|
Control |
1 |
|
1.82 |
|
|
1267520 |
|
2 |
|
1.88 |
|
|
1530368 |
|
|
3 |
|
1.86 |
|
|
1407110 |
|
|
4 |
|
1.87 |
|
|
1472487 |
|
|
5 |
|
1.86 |
|
|
1446346 |
|
|
6 |
|
1.84 |
|
|
1346771 |
|
|
Mean |
|
1.86 |
|
|
1411767 |
|
3) 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 hours) |
SD ± |
CV |
Mean CV [%] |
||
section-by-section |
||||||||
0 - 24 hours |
24 - 48 hours |
48 - 72 hours |
||||||
Control |
1 |
1.30 |
2.22 |
1.95 |
1.82 |
0.474 |
26.1 |
23.9 |
2 |
1.48 |
2.07 |
2.10 |
1.88 |
0.352 |
18.7 |
||
3 |
1.34 |
2.24 |
1.98 |
1.86 |
0.463 |
24.9 |
||
4 |
1.41 |
2.14 |
2.06 |
1.87 |
0.397 |
21.2 |
||
5 |
1.33 |
2.24 |
2.03 |
1.86 |
0.475 |
25.5 |
||
6 |
1.27 |
2.21 |
2.04 |
1.84 |
0.497 |
27.0 |
||
|
|
|
Mean |
1.86 |
|
|
||
|
|
|
SD ± |
0.02 |
|
|||
|
|
|
CV [%] |
1.21 |
|
4) Environmental Conditions
Initial measured test item concentration |
pH-values |
||
[µg/L] |
Start; 0 hours |
End; 72 hours |
|
634 |
7.59 |
7.60 |
|
207 |
7.60 |
7.89 |
|
61.2 |
7.64 |
8.30 |
|
20.0 |
7.64 |
8.45 |
|
6.34 |
7.70 |
8.53 |
|
2.00 |
7.75 |
8.60 |
|
Control |
8.11 |
8.71 |
|
Room temperature [°C]: |
min.: 22.0 |
max.: 23.0 |
mean value: 22.5 |
Light intensity |
n = 23 |
mean value: 5834 range of the measured values: 5143 to 6342 equalling -11.9 to 8.71% |
CV [%]: 6.63% |
5) Measured Concentration of the test material in the Definitive
Test with Algae
Sampling date |
Fresh Media, |
Old Media, |
|
Dilution of the saturated Solution [%] |
Test Item |
||
Meas. conc. [mg/L] |
Meas. conc. [mg/L] |
% |
|
100 |
0.634 |
0.625 |
99 |
31.6 |
0.207 |
0.175 |
85 |
10.0 |
0.0612 |
0.0564 |
92 |
3.16 |
< LOQ |
0.0305 |
n.a. |
1.00 |
< LOQ |
< LOQ |
n.a. |
0.316 |
< LOQ |
< LOQ |
n.a. |
Control |
< LOQ |
< LOQ |
|
Meas. conc. = measured concentration of the test item, dilution factors taken into account % = percent of the initial measured concentration of the test item LOQ = limit of quantification (25 µg test item /L) n.a. = not applicable |
Description of key information
The EC50-values with confidence interval for inhibition of growth rate (ErC50) was 363 (314 – 425) µg/L. The EC10-values with confidence interval for inhibition of growth rate (ErC10) was 85.0 (57.7 – 113) µg/L.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 363 µg/L
- EC10 or NOEC for freshwater algae:
- 85 µg/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.
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