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EC number: 300-723-4 | CAS number: 127823-21-6
- 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:
- 2018-04-19 to 2018-
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- In the absence of analytical method described and provided by the Sponsor, a method has been developed and validated according to the protocol as specified in the Standard Operating Procedure "MSG-MO-001 Traitement d'une demande d'analyse en BPL".
- Vehicle:
- no
- Details on test solutions:
- PREPARATION OF TEST SOLUTIONS
For both range-finding test and definitive tests, as the test item was known to be difficult to dissolve, a saturated solution was prepared using slow-stirring conditions described in the OECD 123 guideline.
The method used a special temperature controlled glass-jacketed test vessel (around 1000 mL of capacity) with a glass blade at its top. A known volume of test item (1000 µL) was first poured into the flask, then a known quantity of test medium (1000 mL which corresponds to a loading rate of 1 g/L) was gently added. The solution was stirred at 20°C with the glass blade at a speed avoiding formation of an emulsion. A speed of approximately 200 rpm was set up in order to create a vortex depth of around 0.5 cm: the aqueous phase was kept under stirring during approximately 26 hours, and then drawn off as a clear solution after a rest phase of a few minutes without agitation. Tests solutions were then prepared from dilutions of this saturated solution.
The pH of the test solutions were not adjusted. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST SPECIES
The test organism used for the study was Pseudokirchneriella subcapitata, Strain No. CCAP 278/4, supplied by the Culture Centre of Algae and Protozoa (Ambleside, UK).
Transfers of P. subcapitata were made regularly to provide suitable subcultures. The algae were cultivated under standardized conditions as described in Annex 2 of the OECD 201 guideline.
The quality of the stock culture was checked for the absence of micro-organisms and deformed or abnormal cells under microscopic observation before use.
Four days before the start of the exposure, two pre-cultures were prepared by inoculating sufficient cells from the algal stock culture to the growth medium to obtain a low cell density of 104 cells/mL for pre-culturing, in order to maintain exponential growth until the start of the test. The pre-cultures were incubated under the same conditions as those used for the test cultures. Only one of the two pre-cultures was used to inoculate the test flasks for the study. The second one was only to be used if the first one was damaged.
At the beginning of the test, the cell density of the pre-culture was determined. The result was used to calculate the volume to be introduced into each test flask in order to obtain an initial cell concentration of 5.103 cells/mL as recommended in the OECD 201 guideline. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- Temperature was maintained at 23 ± 1°C:
¿ Range-finding test: range from 22.0 to 22.5°C (mean: 22.2°C)
¿ Definitive test: range from 22.0 to 22.5°C (mean: 22.2°C) - Dissolved oxygen:
- 8.3 - 8.5 mg/L (range-finding test)
8.7 - 9.0 mg/L (definitive test) - Nominal and measured concentrations:
- Nominal concentrations: 0 (Control), 2.4, 3.8, 6.0, 9.6, 15.6, 25.0, 40.0 (% saturated stock solution)
Measured concentrations: see "Any other information on results incl. tables". - Details on test conditions:
- See "Any other information on materials and methods incl. tables".
- Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.55 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1.15 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.16 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.5 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield
- Details on results:
- See "Any other information on results incl. tables".
- Validity criteria fulfilled:
- yes
- Conclusions:
- DISCUSSION/CONCLUSION
The results are reported as growth rate and yield inhibitions. The concentrations that result in a 10 and 50% reduction in growth rate (72h-ErC10 and 72h-ErC50, respectively) and yield (72h-EyC10 and 72h-EyC50, respectively) were determined.
Chemical analysis of the test item showed the instability of the substance over the 72-hour test period. Based on these results, the exposure concentrations were based on the geometric mean of measured concentrations.
Growth rate:
72-h ErC10 = 0.55 mg/L (95% confidence level: 0.48 – 0.63 mg/L)
72-h ErC50 = 1.15 mg/L (95% confidence level: 0.98 – 1.35 mg/L)
Yield:
72-h EyC10 = 0.16mg/L (95% confidence level: 0.11 – 0.25 mg/L)
72-h EyC50 = 0.50 mg/L (95% confidence level: 0.31 – 0.83 mg/L) - Executive summary:
This study was designed to determine the effects of the test item on the growth ofPseudokirchneriella subcapitatain a 72-hour test according to the OECD 201 Guideline.
As the test item was known to be difficult to dissolve, tests solutions were prepared from dilutions of a saturated solutionprepared using slow-stirring conditionsdescribed in the OECD 123 guideline.
Chemical analysis of the test item showed the instability of the substance over the 72-hour test period. Based on these results, the exposure concentrations were based on the geometric mean of measured concentrations.
The results are reported as growth rate and yield inhibitions. The concentrations that result in a 10 and 50% reduction in growth rate (72h-ErC10 and 72h-ErC50, respectively) and yield (72h-EyC10 and 72h-EyC50, respectively) were determined.
Growth Function
72h-EC10(mg/L)
95% confidence level
72h-EC50
(mg/L)
95% confidence level
Lower limit
Upper limit
Lower limit
Upper limit
Growth rate
0.55
0.48
0.63
1.15
0.98
1.35
Yield
0.16
0.11
0.25
0.50
0.31
0.83
The definitive test met the validity criteria of the test guideline detailed as follows:
§ The biomass in the control cultures increased exponentially by a factor of 74.5 within the 72-hour test period (required: at last 16-fold)
§ The mean coefficients of variation for section-by-section specific growth rates (days 0-1, 1-2 and 2-3) in the control cultures were less than or equal to 16.3 (required: < 35%)
§ The coefficient of variation of average specific growth rates during the whole test period in the control cultures was 2.7% (required: < 7%)
Reference
Results and discussion
Table1Test item determination at T0 (Range-finding test)
Test solution (% saturated stock solution) |
Test item concentration(mg/L) |
Mean |
SD |
RSD (%) |
||
Measure 1 |
Measure 2 |
Measure 3 |
||||
Control |
< DL |
< DL |
< DL |
< DL |
NA |
NA |
10.0 |
2.29 |
1.74 |
1.45 |
1.83 |
0.428 |
23.4 |
25.0 |
2.64 |
3.37 |
3.59 |
3.20 |
0.499 |
15.6 |
50.0 |
6.56 |
7.66 |
7.24 |
7.16 |
0.555 |
7.8 |
100.0 |
13.16 |
8.88 |
10.29 |
10.78 |
2.178 |
20.2 |
< DL (0.033 mg/L): concentration lower than the Detection Limit
< QL (0.109 mg/L): concentration lower than the Quantification Limit
NA: Not Applicable
Table2Test item determination at 72h (Range-finding test)
Test solution (% saturated stock solution) |
Test item concentration(mg/L) |
Mean |
SD |
RSD (%) |
||
Measure 1 |
Measure 2 |
Measure 3 |
||||
Control |
< DL |
< DL |
< DL |
< DL |
NA |
NA |
10.0 |
0.32 |
0.33 |
0.40 |
0.35 |
0.041 |
11.7 |
25.0 |
0.90 |
0.79 |
0.83 |
0.84 |
0.056 |
6.7 |
50.0 |
2.60 |
2.94 |
2.76 |
2.77 |
0.174 |
6.3 |
100.0 |
4.22 |
3.55 |
3.12 |
3.63 |
0.553 |
15.2 |
< DL (0.033 mg/L): concentration lower than the Detection Limit
< QL (0.109 mg/L): concentration lower than the Quantification Limit
NA: Not Applicable
Table3Measured test item concentrations evolution (Range-finding test)
Test solution (% saturated stock solution) |
Test item concentration(mg/L) |
Deviation of 72h measured conc. from 0h (%) |
|
T0 |
T72h |
||
Control |
< DL |
< DL |
NA |
10.0 |
1.83 |
0.35 |
-80.9 |
25.0 |
3.2 |
0.84 |
-73.8 |
50.0 |
7.16 |
2.77 |
-61.3 |
100.0 |
10.78 |
3.63 |
-66.3 |
< DL (0.033 mg/L): concentration lower than the Detection Limit
< QL (0.109 mg/L): concentration lower than the Quantification Limit
NA: Not Applicable
Table4Test item determination at T0 (Definitive test)
Test solution (% saturated stock solution) |
Test item concentration(mg/L) |
Mean |
SD |
RSD (%) |
||
Measure 1 |
Measure 2 |
Measure 3 |
||||
Control |
< DL |
< DL |
< DL |
< DL |
NA |
NA |
2.4 |
0.20 |
0.21 |
0.22 |
0.21 |
0.012 |
5.7 |
3.8 |
0.29 |
0.30 |
0.30 |
0.29 |
0.006 |
2.1 |
6.0 |
0.48 |
0.53 |
0.47 |
0.50 |
0.033 |
6.6 |
9.6 |
0.74 |
0.73 |
0.70 |
0.73 |
0.023 |
3.1 |
15.6 |
1.20 |
1.23 |
1.21 |
1.21 |
0.018 |
1.5 |
25.0 |
1.59 |
1.98 |
1.90 |
1.83 |
0.207 |
11.3 |
40.0 |
2.92 |
2.85 |
2.80 |
2.86 |
0.060 |
2.1 |
< DL (0.010 mg/L): concentration lower than the Detection Limit
< QL (0.033 mg/L): concentration lower than the Quantification Limit
NA: Not Applicable
Table5Test item determination at 72h (Definitive test)
Test solution (% saturated stock solution) |
Test item concentration(mg/L) |
Mean |
SD |
RSD (%) |
||
Measure 1 |
Measure 2 |
Measure 3 |
||||
Control |
< DL |
< DL |
< DL |
< DL |
NA |
NA |
2.4 |
0.04 |
- |
0.04 |
0.04 |
0.00003 |
0.1 |
3.8 |
0.07 |
0.07 |
0.06 |
0.06 |
0.003 |
4.3 |
6.0 |
0.10 |
0.10 |
0.10 |
0.10 |
0.004 |
3.9 |
9.6 |
0.16 |
0.18 |
0.17 |
0.17 |
0.009 |
5.2 |
15.6 |
0.29 |
0.34 |
0.33 |
0.32 |
0.026 |
8.2 |
25.0 |
0.60 |
0.68 |
0.62 |
0.63 |
0.041 |
6.5 |
40.0 |
1.03 |
0.92 |
1.22 |
1.06 |
0.154 |
14.6 |
< DL (0.010 mg/L): concentration lower than the Detection Limit
< QL (0.033 mg/L): concentration lower than the Quantification Limit
NA: Not Applicable
- not analysed (analytical device deficiency)
Table6Test item determination – Concentrations used for statistical analysis (Definitive test)
Test solution (% saturated stock solution) |
Test item concentration(mg/L) |
Deviation of 72h measured conc. from 0h (%) |
Mean measured conc. (mg/L)* |
|
T0 |
T72h |
|||
Control |
< DL |
< DL |
NA |
NA |
2.4 |
0.21 |
0.04 |
-81.0 |
0.09 |
3.8 |
0.29 |
0.06 |
-79.3 |
0.13 |
6.0 |
0.50 |
0.10 |
-80.0 |
0.22 |
9.6 |
0.73 |
0.17 |
-76.7 |
0.35 |
15.6 |
1.21 |
0.32 |
-73.6 |
0.62 |
25.0 |
1.83 |
0.63 |
-65.6 |
1.07 |
40.0 |
2.86 |
1.06 |
-62.9 |
1.74 |
< DL (0.010 mg/L): concentration lower than the Detection Limit
< QL (0.033 mg/L): concentration lower than the Quantification Limit
NA: Not Applicable
* Concentrations extrapolated as geometric mean of measured concentrations
Table7Algal cell density (Range-finding test)
Test solution |
Replicate |
Algal density at 24h (Fd, ¢ *104/ ml ) |
Algal density at 48h (Fd, ¢ *104/ ml ) |
Algal density at 72h (Fd, ¢ *104/ ml ) |
Average specific growth rate J0-J3 |
Specific growth rate inhibition (%) |
||||||||||
Replicate mean |
Mean |
RSD |
Replicate mean |
Mean |
RSD |
Replicate mean |
Mean |
RSD |
Replicate mean |
Average |
Sx |
CV |
||||
Control |
a |
2,46 |
2,56 |
10,20 |
11,09 |
10,58 |
7,58 |
61,36 |
58,33 |
6,71 |
1,603 |
1,586 |
0,023 |
1,443 |
Inhibition |
Inhibition |
b |
2,76 |
11,53 |
62,82 |
1,611 |
||||||||||||
c |
2,94 |
11,21 |
57,45 |
1,581 |
||||||||||||
d |
2,64 |
9,52 |
51,70 |
1,546 |
||||||||||||
e |
2,33 |
10,03 |
57,24 |
1,580 |
||||||||||||
f |
2,26 |
10,10 |
59,44 |
1,593 |
||||||||||||
10,00 |
a |
1,04 |
0,99 |
5,40 |
4,09 |
3,68 |
11,22 |
22,42 |
19,33 |
16,28 |
1,268 |
1,215 |
0,055 |
4,531 |
20,1 |
23,4 |
b |
0,94 |
3,27 |
16,13 |
1,158 |
27,0 |
|||||||||||
c |
0,99 |
3,68 |
19,45 |
1,220 |
23,0 |
|||||||||||
25,00 |
a |
0,92 |
0,91 |
2,39 |
1,63 |
1,55 |
4,61 |
4,36 |
3,86 |
12,53 |
0,722 |
0,680 |
0,042 |
6,134 |
54,5 |
57,1 |
b |
0,92 |
1,52 |
3,40 |
0,639 |
59,7 |
|||||||||||
c |
0,88 |
1,50 |
3,82 |
0,678 |
57,3 |
|||||||||||
50,00 |
a |
0,82 |
0,84 |
2,24 |
0,72 |
0,65 |
9,44 |
0,13 |
0,12 |
7,80 |
-0,443 |
-0,464 |
0,026 |
-5,705 |
127,9 |
129,3 |
b |
0,85 |
0,63 |
0,13 |
-0,456 |
128,7 |
|||||||||||
c |
0,86 |
0,60 |
0,11 |
-0,494 |
131,1 |
|||||||||||
100,00 |
a |
0,73 |
0,73 |
0,94 |
0,15 |
0,15 |
13,88 |
0,04 |
0,04 |
12,79 |
-0,840 |
-0,811 |
0,041 |
-5,104 |
153,0 |
151,1 |
b |
0,72 |
0,14 |
0,04 |
-0,829 |
152,3 |
|||||||||||
c |
0,74 |
0,18 |
0,05 |
-0,764 |
148,2 |
Table8Algal cell density (Definitive test)
Test solution |
Replicate |
Algal density at 24h (Fd, ¢ *104/ ml ) |
Algal density at 48h (Fd, ¢ *104/ ml ) |
Algal density at 72h (Fd, ¢ *104/ ml ) |
Average specific growth rate J0-J3 |
Specific growth rate inhibition (%) |
||||||||||
Replicate mean |
Mean |
RSD |
Replicate mean |
Mean |
RSD |
Replicate mean |
Mean |
RSD |
Replicate mean |
Average |
Sx |
CV |
||||
Control |
a |
1,88 |
1,67 |
13,16 |
8,04 |
7,04 |
13,19 |
36,78 |
37,22 |
12,41 |
1,433 |
1,435 |
0,039 |
2,745 |
Inhibition |
Inhibition |
b |
1,97 |
8,09 |
37,85 |
1,442 |
||||||||||||
c |
1,71 |
7,17 |
36,61 |
1,431 |
||||||||||||
d |
1,41 |
5,74 |
32,94 |
1,396 |
||||||||||||
e |
1,54 |
6,36 |
33,40 |
1,401 |
||||||||||||
f |
1,52 |
6,87 |
45,76 |
1,506 |
||||||||||||
2,40 |
a |
1,33 |
1,31 |
2,29 |
6,85 |
6,49 |
4,94 |
31,02 |
29,25 |
7,18 |
1,376 |
1,356 |
0,024 |
1,790 |
4,1 |
5,5 |
b |
1,28 |
6,23 |
26,93 |
1,329 |
7,4 |
|||||||||||
c |
1,33 |
6,39 |
29,80 |
1,363 |
5,0 |
|||||||||||
3,80 |
a |
1,32 |
1,27 |
4,80 |
6,43 |
6,41 |
0,39 |
33,91 |
31,95 |
5,30 |
1,406 |
1,385 |
0,017 |
1,258 |
2,0 |
3,4 |
b |
1,20 |
6,38 |
30,88 |
1,374 |
4,2 |
|||||||||||
c |
1,27 |
6,43 |
31,08 |
1,377 |
4,1 |
|||||||||||
6,00 |
a |
1,27 |
1,09 |
14,42 |
5,90 |
5,58 |
5,36 |
31,06 |
29,82 |
4,90 |
1,376 |
1,362 |
0,016 |
1,211 |
4,1 |
5,0 |
b |
0,98 |
5,31 |
30,19 |
1,367 |
4,7 |
|||||||||||
c |
1,02 |
5,53 |
28,21 |
1,344 |
6,3 |
|||||||||||
9,60 |
a |
0,81 |
0,94 |
12,18 |
4,52 |
4,64 |
2,31 |
22,73 |
23,71 |
10,66 |
1,272 |
1,285 |
0,035 |
2,703 |
11,3 |
10,4 |
b |
1,04 |
4,72 |
21,82 |
1,259 |
12,3 |
|||||||||||
c |
0,95 |
4,69 |
26,59 |
1,325 |
7,7 |
|||||||||||
15,60 |
a |
0,78 |
0,76 |
5,64 |
3,30 |
3,10 |
5,48 |
16,18 |
15,89 |
3,11 |
1,159 |
1,153 |
0,010 |
0,909 |
19,2 |
19,7 |
b |
0,78 |
3,00 |
16,16 |
1,159 |
19,2 |
|||||||||||
c |
0,71 |
3,01 |
15,31 |
1,141 |
20,5 |
|||||||||||
25,00 |
a |
0,65 |
0,66 |
3,12 |
1,56 |
1,65 |
7,01 |
5,54 |
6,09 |
13,21 |
0,802 |
0,832 |
0,043 |
5,136 |
44,1 |
42,0 |
b |
0,64 |
1,78 |
7,02 |
0,880 |
38,6 |
|||||||||||
c |
0,68 |
1,61 |
5,73 |
0,813 |
43,4 |
|||||||||||
40,00 |
a |
0,63 |
0,63 |
0,42 |
0,86 |
0,85 |
2,48 |
1,02 |
1,15 |
10,60 |
0,237 |
0,277 |
0,036 |
13,040 |
83,5 |
80,7 |
b |
0,64 |
0,87 |
1,19 |
0,288 |
79,9 |
|||||||||||
c |
0,63 |
0,83 |
1,26 |
0,307 |
78,6 |
Table9Percentage of inhibition (Range-finding test)
Test solution (% saturated stock solution) |
Growth rate Iµi (%) |
YieDL Iyi (%) |
10.0 |
23.4 |
67.4 |
25.0 |
57.1 |
94.2 |
50.0 |
>100 |
>100 |
100.0 |
>100 |
>100 |
Iµi: average percentage inhibition of growth rate
Iyi: average percentage inhibition of yieDL
Table10Percentage of inhibition (Definitive test)
Test solution (% saturated stock solution) |
Growth rate Iµi (%) |
YieDL Iyi (%) |
2.4 |
5.5 |
21.7 |
3.8 |
3.4 |
14.4 |
6.0 |
5.0 |
20.2 |
9.6 |
10.4 |
36.8 |
15.6 |
19.7 |
58.1 |
25.0 |
42.0 |
84.8 |
40.0 |
80.7 |
98.2 |
Iµi: average percentage inhibition of growth rate
Iyi: average percentage inhibition of yieDL
Table11Measured pH and dissolved oxygen (Range-finding test)
Test solution (% saturated stock solution) |
pH |
Dissolved O2 (mg/L) |
||
0h |
72h |
0h |
72h |
|
Control |
7.9 |
7.9 |
8.4 |
8.5 |
10.0 |
8.0 |
7.9 |
8.3 |
8.4 |
25.0 |
8.0 |
7.9 |
8.3 |
8.4 |
50.0 |
8.0 |
7.9 |
8.3 |
8.3 |
100.0 |
7.9 |
7.9 |
8.4 |
8.3 |
Table12Measured pH and dissolved oxygen (Definitive test)
Test solution (% saturated stock solution) |
pH |
Dissolved O2 (mg/L) |
||
0h |
72h |
0h |
72h |
|
Control |
7.9 |
8.0 |
9.0 |
8.8 |
2.4 |
7.9 |
8.0 |
9.0 |
8.8 |
3.8 |
7.9 |
8.0 |
9.0 |
8.8 |
6.0 |
7.9 |
8.0 |
9.0 |
8.8 |
9.6 |
7.9 |
8.0 |
9.0 |
8.8 |
15.6 |
7.9 |
7.9 |
9.0 |
8.8 |
25.0 |
7.9 |
7.9 |
9.0 |
8.7 |
40.0 |
7.9 |
7.9 |
9.0 |
8.7 |
NA: Not Applicable
Reference item test
The sensitivity of the test system and the methodology are evaluated every two months by performing an algal growth inhibition test on potassium dichromate. The latest value of ErC50 obtained in April 2018 was 1.15 mg/L.
For information, according to ISO 8692 standard, 72h-ErC50 obtained from an inter-laboratory exercise on potassium dichromate was in the 0.65 to 1.73 mg/L range.
Range-finding test
The appearance of the test solutions was visually checked at the beginning and at the end of the test. Solutions were found to be clear, no precipitation was observed at the end of the test.
Microscopic observation confirmed that the algae appeared "normal" at the end of the test: the normal shape ofP. subcapitataalgae is a crescent shaped cell with an average length of 5-10 µm.
The analytical results data are presented inTable1toTable3. Chemical analysis of test samples taken at 0 and 72 h indicated that concentrations of the test item were not maintained over the 72h test period (i.e. deviation > 20%). The instability of the substance was thus confirmed over the test period.
The examination of growth plots shows exponential growth of control culture at the expected rate throughout the test.
Cell densities, biomass, and growth rate are summarised inTable7, percentages of inhibition inTable9.The results (growth rate) demonstrated that algal growth was significantly inhibited from the lowest tested concentration.
Definitive test
The appearance of the test solutions was visually checked at the beginning and at the end of the test. Solutions were found to be clear, no precipitation was observed at the end of the test.
Microscopic observation confirmed that the algae appeared "normal" at the end of the test: the normal shape ofP. subcapitataalgae is a crescent shaped cell with an average length of 5-10 µm.
The analytical results data are presented in Table 4toTable6. Chemical analysis of test samples taken at 0 and 72 h indicated that concentrations of the test item were not maintained over the 72h test period (i.e. deviation > 20%). As a consequence, the stability of the substance was not confirmed over the test period. Based on these results, the exposure concentrations were based on the geometric mean of measured concentrations.
The examination of growth plots shows exponential growth of control culture at the expected rate throughout the test.
Cell densities, biomass, and growth rate throughout the test period are summarised inTable8. The percentages of inhibition are presented inTable10.The results (growth rate) demonstrated that algal growth was inhibited from 3.4% to 80.7% at the highest tested concentration.
Environmental conditions
Dissolved oxygen and pH are presented inTable11&Table12. Measurements were carried out in non-inoculated solution at T0and inoculated solution at T72.
The light intensity was measured as follows:
§ Range-finding test: range from 108 to 110 µE.m².s-1
§ Definitive test: range from 108 to 119 µE.m².s-1
Statistical analysis
Statistical analysis was performed with the software ToxRat®version 3.2.1.
Validation criteria
The definitive test met the validity criteria of the test guideline detailed as follows:
§ The biomass in the control cultures increased exponentially by a factor of 74.5 within the 72-hour test period (required: at last 16-fold)
§ The mean coefficients of variation for section-by-section specific growth rates (days 0-1, 1-2 and 2-3) in the control cultures were less than or equal to 16.3 (required: < 35%)
§ The coefficient of variation of average specific growth rates during the whole test period in the control cultures was 2.7% (required: < 7%)
Description of key information
The toxicity of the test substance to Pseudokirchneriella subcapitata was determined in an experimental study performed in accordance with the OECD 201 test guideline and GLP requirements.
The 72h-ErC50 was equal to 1.15 mg/L and the 72h-ErC10 was equal to 0.55 mg/L.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 1.15 mg/L
- EC10 or NOEC for freshwater algae:
- 0.55 mg/L
Additional information
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