Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
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.
EC number: 202-216-2 | CAS number: 93-08-3
- 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:
- Study Initiation Date: November 24, 2020 to Study Completion Date: May 20, 2021
- 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:
- - Concentrations: 0.8, 1.6, 3.2, 6.4, 12.8 mg/L
- Sampling method: Test item formulation prepared in volumetric flask as stock, then respective volumes of solution were transferred from flask to measuring cylinder to obtain the required concentrations for the study. - Vehicle:
- yes
- Remarks:
- Acetone
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: 12.5 mg of test item was dissolve in 50 µL acetone and made up to 500 mL in a volumetric flask using OECD medium (stock). 10 mL, 21.67 mL, 48.33 mL, 106.67 mL, 235 mL from stock solution were transferred into 500 mL measuring cylinder and made up to 35 mL using OECD medium. Hence concentrations of 0.8, 1.6, 3.2, 6.4, 12.8 mg/L were achieved.
- Controls: OECD medium
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Acetone
- Concentration of vehicle in test medium (stock solution and final test solution(s) or suspension(s) including control(s)): 0.1ml/L - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Green algae
- Strain: ATCC
- Source (laboratory, culture collection): Initially procured from “American Type Culture Collection”, Chromachemie Laboratory Private Limited, later test system was sub-cultured in the test facility.
- Age of inoculum (at test initiation): 3-4 days before start of the test.
- Method of cultivation:The required volume of OECD growth medium was prepared as per OECD 201, test system was sub-cultured using OECD medium.
ACCLIMATION
- Culturing media and conditions (same as test or not):Yes
- Any deformed or abnormal cells observed: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 21.7 – 23.9 °C
- pH:
- 7.6-8.1
- Nominal and measured concentrations:
- Nominal
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 mL conical flasks
- Type (delete if not applicable): open / closed Sterilized, flasks were covered with cap
- Material, size, headspace, fill volume: Conical flasks were made of glass. Volume capacity 250 mL.
- Aeration: no aeration
- Initial cells density: 10000 cells/ ml
- Control end cells density: 10000 cells/ml
- No. of organisms per vessel: 10000 cells/mL
- No. of vessels per concentration (replicates): Range finding study: 3 replicates/test item concentration
Main Study: 3 replicates/test item concentration
- No. of vessels per control (replicates): 6 replicates for control group during range finding and main study.
- No. of vessels per vehicle control (replicates):6 replicates for control group during range finding and main study.
GROWTH MEDIUM
- Standard medium used: yes Yes (OECD Medium as per OECD 201)
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water:
- Total organic carbon:
- Particulate matter:
- Metals:
- Pesticides:
- Chlorine:
- Alkalinity:
- Ca/mg ratio:
- Conductivity:
- Culture medium different from test medium: NO
- Intervals of water quality measurement:
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH:no
- Photoperiod:Continuous light for test system
- Light intensity and quality:Average: 6766-6794 Lux
- Salinity (for marine algae):
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: The cells were counted using Haemocytometer under illumination of the microscope at 24, 48, and 72 h after inoculation.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Range finding study Yes
- Test concentrations: 0 (control), 0 (vehicle control), 1.5, 3, 6, 12, 24 mg/L
- Results used to determine the conditions for the definitive study: Based on the results of range finding test following concentrations of 0 (control), 0 (vehicle control), 0.8, 1.6, 3.2, 6.4, 12.8 mg/L were selected for the main study as significant changes (inhibition algal growth rate) were observed in treatment groups during 72h test period. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 6.19 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% CI 5.43 mg/L and 6.95 mg/L.
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.73 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield
- Remarks on result:
- other: 95% CI 2.42 mg/L and 3.04 mg/L
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.6 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 Yes (64.25, 62.58 times of the initial cell count in control and vehicle control, respectively)
- Results with reference substance (positive control):
- - Results with reference substance valid Yes
- EC50:
ErC50 (72h) = 0.620 mg/L (growth rate)
EyC50 (72h) = 0.334 mg/L (yield) - Reported statistics and error estimates:
- 72h EC50 value with 95% confidence limits (upper limit, lower limit) were calculated by probit analysis using NCSS Software 2019, version 19.0.3.
The NOEC and LOEC value were calculated using the One-way Analysis of Variance - Kruskal - Wallis - Comparison Z-Value test. - Validity criteria fulfilled:
- yes
- Remarks:
- The control and vehicle control increased by 64.25, 62.58 times (>16 times) of the initial cell count. The mean CoV for growth rate for the control cultures was 32.8%. The coefficient of variation of average specific growth rate was 0.6%.
- Conclusions:
- The effect of test chemical on fresh water algae was studied as per OECD 201 test guidelines, the 72-h EC50 of test item to alga on growth rate and yield are 6.19, 2.73 mg/L, respectively. 72-h LOEC of test item to alga on growth rate and yield is 3.2 mg/L. 72-h NOEC of test item to alga on growth rate and yield is 1.6 mg/L.
- Executive summary:
This study was conducted as per OECD 201 (2011) to assess the acute toxicity effects of test chemical on the growth of green alga Pseudokirchneriella subcapitata(ATCC)following exposure of alga up to 72 h under static condition. Test system was initially procured from “American Type Culture Collection”, Chromachemie Laboratory Private Limited, later test system was sub-cultured (using OECD growth medium, OECD 201) in the test facility. 250 mL sterilized conical flasks covered with cap were used in the study. The test item was found to be soluble in acetone. Hence, acetone (concentration <0.1mL/L) with OECD growth medium was used as test medium. An inoculum culture in the test medium was prepared 3-4 days prior to test and culture conditions were maintained same as the test conditions. A range finding study (3 replicates/ concentration, 6 replicates for control group)with the test concentrations of1.5, 3, 6, 12, 24 mg/L were tested along with a control (0), vehicle control (0) group, prior to the main study. The inhibition in growth rate (0%, 0%, 3.04%, 22.18%, 31.09%, 87.92%, 100%) and yield (0%, 0%, 11.69%, 60.46%, 73.02%, 98.85%, 100%) were observed at 72 h in the test concentrations of 0, 0, 1.5, 3, 6, 12, 24 mg/L. Based on the results of range finding test following concentrations of 0 (control), 0 (vehicle control), 0.8, 1.6, 3.2, 6.4, 12.8 mg/L were selected for the main study(3 replicates/ concentration, 6 replicates for control groups)as significant changes (inhibition algal growth rate) were observed in treatment groups during 72h test period. The inhibition in growth rate (0%, 0%, 1.78%, 6.68%, 24.76%, 33.68%, 90.82%) and yield (0%, 0%, 7.17%, 24.49%, 65.09%, 76.32%, 99.19%) were observed during 72h test period in the test concentrations of 0 (control), 0 (vehicle control), 0.8, 1.6, 3.2, 6.4, 12.8 mg/L. A reference standard (Potassium dichromate) was tested to ensure the authenticity of the test in the lab. And the inhibition of growth rate (ErC50-72h) and yield (EyC50-72h) were found to be 0.620 mg/L & 0.334 mg/L, respectively; and were found to be in acceptable range. The initial cell density was 10000 cells/mL.The algal cells in the control and vehicle control increased by 64.25, 62.58 times (>16 times) of the initial cell count during the 72-h exposure period, respectively. The mean coefficient of variation for section-by-section growth rate for the control cultures over the test period (0-72-h) was 32.8% (<35%). The coefficient of variation of average specific growth rate was 0.6% (<7%). Hence, fulfilling the all the validity criteria of the test. HPLC method was used for method validation and active ingredient analysis along with stability of the test item in the test medium. Test item was found to be stable in the test medium. The active ingredient content results were considered acceptable (80-120%) as during main study 0 hr and 72 hr avg. recovery for 0.8, 3.2, 12.8 mg/L conc were 94.34%, 94.44%, 95.84% & 94.11%, 94.59%, 96.11%, respectively, were found in acceptable range. Continuous light having and average light intensity of 6766-6794 Lux, pH of 7.6-8.1, temperature 21.7-23.9 °C along with a shaking speed of 110 RPM were provided and maintained for the test system throughout the test. 72h EC50 (growth rate and yield) values with 95% confidence limits were calculated by probit analysis. NOEC and LOEC of growth rate and yield were calculated by one way ANOVA (Kruskal-Wallis-Comparison Z-Value Test) using NCSS Software 2019, version 19.0.3. The cells were counted using Haemocytometer under illumination of the microscope at 24, 48, and 72 h after inoculation. 72-h EC50 of test item to alga on growth rate and yield are 6.19, 2.73 mg/L, respectively. 72-h LOEC of test item to alga on growth rate and yield is 3.2 mg/L. 72-h NOEC of test item to alga on growth rate and yield is 1.6 mg/L. Thus based on the outcomes test chemical was classified into aquatic chronic category 2 as CLP classification criteria.
Reference
Treatments (mg/L) |
R. No |
A |
B |
ln A |
ln B |
(ln B - ln A)/Ocassion |
Inhibition growth rate (%Ir) |
Yield B - A |
Inhibition yield (%Iy) |
||||
Control |
CR1 |
10000 |
27500 |
9.2103 |
10.2219 |
0.04 |
0.00 |
17500 |
0.00 |
||||
CR2 |
10000 |
27500 |
9.2103 |
10.2219 |
0.04 |
0.00 |
17500 |
0.00 |
|||||
CR3 |
10000 |
25000 |
9.2103 |
10.1266 |
0.04 |
0.00 |
15000 |
0.00 |
|||||
CR4 |
10000 |
25000 |
9.2103 |
10.1266 |
0.04 |
0.00 |
15000 |
0.00 |
|||||
CR5 |
10000 |
30000 |
9.2103 |
10.3090 |
0.05 |
0.00 |
20000 |
0.00 |
|||||
CR6 |
10000 |
32500 |
9.2103 |
10.3890 |
0.05 |
0.00 |
22500 |
0.00 |
|||||
Average |
10000 |
27917 |
9.2103 |
10.2325 |
0.04 |
0.00 |
17917 |
0.00 |
|||||
SD |
0 |
2923 |
0.00 |
0.10 |
0.00 |
|
|||||||
% C.V |
0.00 |
10.47 |
0.00 |
1.01 |
10.07 |
|
|||||||
Solventcontrol |
T1R1 |
10000 |
25000 |
9.2103 |
10.1266 |
0.04 |
0.00 |
15000 |
0.00 |
||||
T1R2 |
10000 |
22500 |
9.2103 |
10.0213 |
0.03 |
0.00 |
12500 |
0.00 |
|||||
T1R3 |
10000 |
22500 |
9.2103 |
10.0213 |
0.03 |
0.00 |
12500 |
0.00 |
|||||
T1R4 |
10000 |
25000 |
9.2103 |
10.1266 |
0.04 |
0.00 |
15000 |
0.00 |
|||||
T1R5 |
10000 |
27500 |
9.2103 |
10.2219 |
0.04 |
0.00 |
17500 |
0.00 |
|||||
T1R6 |
10000 |
22500 |
9.2103 |
10.0213 |
0.03 |
0.00 |
12500 |
0.00 |
|||||
Average |
10000 |
24167 |
9.2103 |
10.0898 |
0.04 |
0.00 |
14167 |
0.00 |
|||||
SD |
0 |
2041 |
0.00 |
0.08 |
0.00 |
|
|||||||
% C.V |
0.00 |
8.45 |
0.00 |
0.82 |
9.41 |
|
|||||||
0.8 |
T2R1 |
10000 |
20000 |
9.2103 |
9.9035 |
0.03 |
21.19 |
10000 |
29.41 |
||||
T2R2 |
10000 |
17500 |
9.2103 |
9.7700 |
0.02 |
36.37 |
7500 |
47.06 |
|||||
T2R3 |
10000 |
22500 |
9.2103 |
10.0213 |
0.03 |
7.80 |
12500 |
11.76 |
|||||
Average |
10000 |
20000 |
9.2103 |
9.8982 |
0.03 |
21.78 |
10000 |
29.41 |
|||||
SD |
0 |
2500 |
0.00 |
0.13 |
0.01 |
|
|||||||
% C.V |
0.00 |
12.50 |
0.00 |
1.27 |
18.28 |
|
|||||||
1.6 |
T3R1 |
10000 |
17500 |
9.2103 |
9.7700 |
0.02 |
36.37 |
7500 |
47.06 |
||||
T3R2 |
10000 |
20000 |
9.2103 |
9.9035 |
0.03 |
21.19 |
10000 |
29.41 |
|||||
T3R3 |
10000 |
17500 |
9.2103 |
9.7700 |
0.02 |
36.37 |
7500 |
47.06 |
|||||
Average |
10000 |
18333 |
9.2103 |
9.8145 |
0.03 |
31.31 |
8333 |
41.18 |
|||||
SD |
0 |
1443 |
0.00 |
0.08 |
0.00 |
|
|||||||
% C.V |
0.00 |
7.87 |
0.00 |
0.79 |
12.76 |
|
|||||||
3.2 |
T4R1 |
10000 |
12500 |
9.2103 |
9.4335 |
0.01 |
74.63 |
2500 |
82.35 |
||||
T4R2 |
10000 |
15000 |
9.2103 |
9.6158 |
0.02 |
53.90 |
5000 |
64.71 |
|||||
T4R3 |
10000 |
12500 |
9.2103 |
9.4335 |
0.01 |
74.63 |
2500 |
82.35 |
|||||
Average |
10000 |
13333 |
9.2103 |
9.4943 |
0.01 |
67.72 |
3333 |
76.47 |
|||||
SD |
0 |
1443 |
0.00 |
0.11 |
0.00 |
|
|||||||
% C.V |
0.00 |
10.83 |
0.00 |
1.11 |
37.08 |
|
|||||||
6.4 |
T5R1 |
10000 |
12500 |
9.2103 |
9.4335 |
0.01 |
74.63 |
2500 |
82.35 |
||||
T5R2 |
10000 |
10000 |
9.2103 |
9.2103 |
0.00 |
100.00 |
0 |
100.00 |
|||||
T5R3 |
10000 |
12500 |
9.2103 |
9.4335 |
0.01 |
74.63 |
2500 |
82.35 |
|||||
Average |
10000 |
11667 |
9.2103 |
9.3591 |
0.01 |
83.09 |
1667 |
88.24 |
|||||
SD |
0 |
1443 |
0.00 |
0.13 |
0.01 |
|
|||||||
% C.V |
0.00 |
12.37 |
0.00 |
1.38 |
86.60 |
|
|||||||
12.8 |
T6R1 |
10000 |
10000 |
9.2103 |
9.2103 |
0.00 |
100.00 |
0 |
100.00 |
||||
T6R2 |
10000 |
10000 |
9.2103 |
9.2103 |
0.00 |
100.00 |
0 |
100.00 |
|||||
T6R3 |
10000 |
10000 |
9.2103 |
9.2103 |
0.00 |
100.00 |
0 |
100.00 |
|||||
Average |
10000 |
10000 |
9.2103 |
9.2103 |
0.00 |
100.00 |
0 |
100.00 |
|||||
SD |
0 |
0 |
0.00 |
0.00 |
0.00 |
|
|||||||
% C.V |
0.00 |
0.00 |
0.00 |
0.00 |
0.00 |
|
|||||||
A - 0 hour cell count |
B = 24/48/72 hours cell count |
||||||||||||
Caluclation: Growth rate(µ)=(ln(X24/48/72 hours) - ln(X0/24/48 hours))/ number of days, %Ir=(µcontrol - µTreatment)/µcontrol*100 |
|||||||||||||
Yield(Y)= X24/48/72 hours - X0/24/48 hours), %Iy=(Ycontrol - YTreatment)/Ycontrol*100 |
|||||||||||||
S.D=Standard deviation |
%C.V=Standard deviation/Average×100 |
R=Replication |
Percentage Inhibition of Growth Rate and Yield – 48 hours (Definitive test)
Treatments (mg/L) |
R. No |
A |
B |
ln A |
ln B |
(ln B - ln A)/Ocassion |
Inhibition growth rate (%Ir) |
Yield B - A |
Inhibition yield (%Iy) |
||
Control |
CR1 |
10000 |
142500 |
9.2103 |
11.8671 |
0.06 |
0.00 |
132500 |
0.00 |
||
CR2 |
10000 |
127500 |
9.2103 |
11.7559 |
0.05 |
0.00 |
117500 |
0.00 |
|||
CR3 |
10000 |
140000 |
9.2103 |
11.8494 |
0.05 |
0.00 |
130000 |
0.00 |
|||
CR4 |
10000 |
137500 |
9.2103 |
11.8314 |
0.05 |
0.00 |
127500 |
0.00 |
|||
CR5 |
10000 |
165000 |
9.2103 |
12.0137 |
0.06 |
0.00 |
155000 |
0.00 |
|||
CR6 |
10000 |
137500 |
9.2103 |
11.8314 |
0.05 |
0.00 |
127500 |
0.00 |
|||
Average |
10000 |
141667 |
9.2103 |
11.8581 |
0.06 |
0.00 |
131667 |
0.00 |
|||
SD |
0 |
12517 |
0.00 |
0.09 |
0.00 |
||||||
% C.V |
0.00 |
8.84 |
0.00 |
0.72 |
3.22 |
||||||
Solvent control |
T1R1 |
10000 |
132500 |
9.2103 |
11.7943 |
0.05 |
0.00 |
122500 |
0.00 |
||
T1R2 |
10000 |
120000 |
9.2103 |
11.6952 |
0.05 |
0.00 |
110000 |
0.00 |
|||
T1R3 |
10000 |
145000 |
9.2103 |
11.8845 |
0.06 |
0.00 |
135000 |
0.00 |
|||
T1R4 |
10000 |
135000 |
9.2103 |
11.8130 |
0.05 |
0.00 |
125000 |
0.00 |
|||
T1R5 |
10000 |
135000 |
9.2103 |
11.8130 |
0.05 |
0.00 |
125000 |
0.00 |
|||
T1R6 |
10000 |
157500 |
9.2103 |
11.9672 |
0.06 |
0.00 |
147500 |
0.00 |
|||
Average |
10000 |
137500 |
9.2103 |
11.8279 |
0.05 |
0.00 |
127500 |
0.00 |
|||
SD |
0 |
12649 |
0.00 |
0.09 |
0.00 |
|
|||||
% C.V |
0.00 |
9.20 |
0.00 |
0.77 |
3.49 |
|
|||||
0.8 |
T2R1 |
10000 |
120000 |
9.2103 |
11.6952 |
0.05 |
5.07 |
110000 |
13.73 |
||
T2R2 |
10000 |
107500 |
9.2103 |
11.5852 |
0.05 |
9.27 |
97500 |
23.53 |
|||
T2R3 |
10000 |
135000 |
9.2103 |
11.8130 |
0.05 |
0.57 |
125000 |
1.96 |
|||
Average |
10000 |
120833 |
9.2103 |
11.6978 |
0.05 |
4.97 |
110833 |
13.07 |
|||
SD |
0 |
13769 |
0.00 |
0.11 |
0.00 |
|
|||||
% C.V |
0.00 |
11.39 |
0.00 |
0.97 |
4.58 |
|
|||||
1.6 |
T3R1 |
10000 |
77500 |
9.2103 |
11.2580 |
0.04 |
21.77 |
67500 |
47.06 |
||
T3R2 |
10000 |
70000 |
9.2103 |
11.1563 |
0.04 |
25.66 |
60000 |
52.94 |
|||
T3R3 |
10000 |
80000 |
9.2103 |
11.2898 |
0.04 |
20.56 |
70000 |
45.10 |
|||
Average |
10000 |
75833 |
9.2103 |
11.2347 |
0.04 |
22.66 |
65833 |
48.37 |
|||
SD |
0 |
5204 |
0.00 |
0.07 |
0.00 |
|
|||||
% C.V |
0.00 |
6.86 |
0.00 |
0.62 |
3.45 |
|
|||||
3.2 |
T4R1 |
10000 |
57500 |
9.2103 |
10.9595 |
0.04 |
33.17 |
47500 |
62.75 |
||
T4R2 |
10000 |
47500 |
9.2103 |
10.7685 |
0.03 |
40.47 |
37500 |
70.59 |
|||
T4R3 |
10000 |
42500 |
9.2103 |
10.6573 |
0.03 |
44.72 |
32500 |
74.51 |
|||
Average |
10000 |
49167 |
9.2103 |
10.7951 |
0.03 |
39.46 |
39167 |
69.28 |
|||
SD |
0 |
7638 |
0.00 |
0.15 |
0.00 |
|
|||||
% C.V |
0.00 |
15.53 |
0.00 |
1.42 |
9.65 |
|
|||||
6.4 |
T5R1 |
10000 |
22500 |
9.2103 |
10.0213 |
0.02 |
69.02 |
12500 |
90.20 |
||
T5R2 |
10000 |
22500 |
9.2103 |
10.0213 |
0.02 |
69.02 |
12500 |
90.20 |
|||
T5R3 |
10000 |
17500 |
9.2103 |
9.7700 |
0.01 |
78.62 |
7500 |
94.12 |
|||
Average |
10000 |
20833 |
9.2103 |
9.9375 |
0.02 |
72.22 |
10833 |
91.50 |
|||
SD |
0 |
2887 |
0.00 |
0.15 |
0.00 |
|
|||||
% C.V |
0.00 |
13.86 |
0.00 |
1.46 |
19.95 |
|
|||||
12.8 |
T6R1 |
10000 |
12500 |
9.2103 |
9.4335 |
0.00 |
91.48 |
2500 |
98.04 |
||
T6R2 |
10000 |
12500 |
9.2103 |
9.4335 |
0.00 |
91.48 |
2500 |
98.04 |
|||
T6R3 |
10000 |
10000 |
9.2103 |
9.2103 |
0.00 |
100.00 |
0 |
100.00 |
|||
Average |
10000 |
11667 |
9.2103 |
9.3591 |
0.00 |
94.32 |
1667 |
98.69 |
|||
SD |
0 |
1443 |
0.00 |
0.13 |
0.00 |
|
|||||
% C.V |
0.00 |
12.37 |
0.00 |
1.38 |
86.60 |
|
|||||
A - 0 hour cell count |
B = 24/48/72 hours cell count |
||||||||||
Caluclation: Growth rate(µ)=(ln(X24/48/72 hours) - ln(X0/24/48 hours))/ number of days, %Ir=(µcontrol - µTreatment)/µcontrol*100 |
|||||||||||
Yield(Y)= X24/48/72 hours - X0/24/48 hours), %Iy=(Ycontrol - YTreatment)/Ycontrol*100 |
|||||||||||
S.D=Standard deviation |
%C.V=Standard deviation/Average×100 |
R=Replication |
EC50Value of test item
Response variable based on % inhibition (0-72 h) |
Effective concentration (mg/L) |
95% confidence limits |
||
Lower limit (mg/L) |
Upper Limit (mg/L) |
|||
Growth rate(mg/L) |
ErC50 |
6.19 |
5.43 |
6.95 |
ErC20 |
3.03 |
2.60 |
3.46 |
|
ErC10 |
2.09 |
0.20 |
2.44 |
|
Yield(mg/L) |
EyC50 |
2.73 |
2.42 |
3.04 |
EyC20 |
1.34 |
1.12 |
1.56 |
|
EyC10 |
0.93 |
0.75 |
1.11 |
|
Growth rate (mg/L) |
LOEC |
3.2 |
||
NOEC |
1.6 |
|||
Yield (mg/L) |
LOEC |
3.2 |
||
NOEC |
1.6 |
Key:LC50- Median Lethal Concentration, LOEC – Lowest Observed Effect Concentration,
Description of key information
This study was conducted as per OECD 201 (2011) to assess the acute toxicity effects of test chemical on the growth of green alga Pseudokirchneriella subcapitata(ATCC)following exposure of alga up to 72 h under static condition. Test system was initially procured from “American Type Culture Collection”, Chromachemie Laboratory Private Limited, later test system was sub-cultured (using OECD growth medium, OECD 201) in the test facility. 250 mL sterilized conical flasks covered with cap were used in the study. The test item was found to be soluble in acetone. Hence, acetone (concentration <0.1mL/L) with OECD growth medium was used as test medium. An inoculum culture in the test medium was prepared 3-4 days prior to test and culture conditions were maintained same as the test conditions. A range finding study (3 replicates/ concentration, 6 replicates for control group)with the test concentrations of1.5, 3, 6, 12, 24 mg/L were tested along with a control (0), vehicle control (0) group, prior to the main study. The inhibition in growth rate (0%, 0%, 3.04%, 22.18%, 31.09%, 87.92%, 100%) and yield (0%, 0%, 11.69%, 60.46%, 73.02%, 98.85%, 100%) were observed at 72 h in the test concentrations of 0, 0, 1.5, 3, 6, 12, 24 mg/L. Based on the results of range finding test following concentrations of 0 (control), 0 (vehicle control), 0.8, 1.6, 3.2, 6.4, 12.8 mg/L were selected for the main study(3 replicates/ concentration, 6 replicates for control groups)as significant changes (inhibition algal growth rate) were observed in treatment groups during 72h test period. The inhibition in growth rate (0%, 0%, 1.78%, 6.68%, 24.76%, 33.68%, 90.82%) and yield (0%, 0%, 7.17%, 24.49%, 65.09%, 76.32%, 99.19%) were observed during 72h test period in the test concentrations of 0 (control), 0 (vehicle control), 0.8, 1.6, 3.2, 6.4, 12.8 mg/L. A reference standard (Potassium dichromate) was tested to ensure the authenticity of the test in the lab. And the inhibition of growth rate (ErC50-72h) and yield (EyC50-72h) were found to be 0.620 mg/L & 0.334 mg/L, respectively; and were found to be in acceptable range. The initial cell density was 10000 cells/mL.The algal cells in the control and vehicle control increased by 64.25, 62.58 times (>16 times) of the initial cell count during the 72-h exposure period, respectively. The mean coefficient of variation for section-by-section growth rate for the control cultures over the test period (0-72-h) was 32.8% (<35%). The coefficient of variation of average specific growth rate was 0.6% (<7%). Hence, fulfilling the all the validity criteria of the test. HPLC method was used for method validation and active ingredient analysis along with stability of the test item in the test medium. Test item was found to be stable in the test medium. The active ingredient content results were considered acceptable (80-120%) as during main study 0 hr and 72 hr avg. recovery for 0.8, 3.2, 12.8 mg/L conc were 94.34%, 94.44%, 95.84% & 94.11%, 94.59%, 96.11%, respectively, were found in acceptable range. Continuous light having and average light intensity of 6766-6794 Lux, pH of 7.6-8.1, temperature 21.7-23.9 °C along with a shaking speed of 110 RPM were provided and maintained for the test system throughout the test. 72h EC50 (growth rate and yield) values with 95% confidence limits were calculated by probit analysis. NOEC and LOEC of growth rate and yield were calculated by one way ANOVA (Kruskal-Wallis-Comparison Z-Value Test) using NCSS Software 2019, version 19.0.3. The cells were counted using Haemocytometer under illumination of the microscope at 24, 48, and 72 h after inoculation. 72-h EC50 of test item to alga on growth rate and yield are 6.19, 2.73 mg/L, respectively. 72-h LOEC of test item to alga on growth rate and yield is 3.2 mg/L. 72-h NOEC of test item to alga on growth rate and yield is 1.6 mg/L. Thus based on the outcomes test chemical was classified into aquatic chronic category 2 as CLP classification criteria.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 6.19 mg/L
Additional information
This study was conducted as per OECD 201 (2011) to assess the acute toxicity effects of test chemical on the growth of green alga Pseudokirchneriella subcapitata(ATCC)following exposure of alga up to 72 h under static condition. Test system was initially procured from “American Type Culture Collection”, Chromachemie Laboratory Private Limited, later test system was sub-cultured (using OECD growth medium, OECD 201) in the test facility. 250 mL sterilized conical flasks covered with cap were used in the study. The test item was found to be soluble in acetone. Hence, acetone (concentration <0.1mL/L) with OECD growth medium was used as test medium. An inoculum culture in the test medium was prepared 3-4 days prior to test and culture conditions were maintained same as the test conditions. A range finding study (3 replicates/ concentration, 6 replicates for control group)with the test concentrations of1.5, 3, 6, 12, 24 mg/L were tested along with a control (0), vehicle control (0) group, prior to the main study. The inhibition in growth rate (0%, 0%, 3.04%, 22.18%, 31.09%, 87.92%, 100%) and yield (0%, 0%, 11.69%, 60.46%, 73.02%, 98.85%, 100%) were observed at 72 h in the test concentrations of 0, 0, 1.5, 3, 6, 12, 24 mg/L. Based on the results of range finding test following concentrations of 0 (control), 0 (vehicle control), 0.8, 1.6, 3.2, 6.4, 12.8 mg/L were selected for the main study(3 replicates/ concentration, 6 replicates for control groups)as significant changes (inhibition algal growth rate) were observed in treatment groups during 72h test period. The inhibition in growth rate (0%, 0%, 1.78%, 6.68%, 24.76%, 33.68%, 90.82%) and yield (0%, 0%, 7.17%, 24.49%, 65.09%, 76.32%, 99.19%) were observed during 72h test period in the test concentrations of 0 (control), 0 (vehicle control), 0.8, 1.6, 3.2, 6.4, 12.8 mg/L. A reference standard (Potassium dichromate) was tested to ensure the authenticity of the test in the lab. And the inhibition of growth rate (ErC50-72h) and yield (EyC50-72h) were found to be 0.620 mg/L & 0.334 mg/L, respectively; and were found to be in acceptable range. The initial cell density was 10000 cells/mL.The algal cells in the control and vehicle control increased by 64.25, 62.58 times (>16 times) of the initial cell count during the 72-h exposure period, respectively. The mean coefficient of variation for section-by-section growth rate for the control cultures over the test period (0-72-h) was 32.8% (<35%). The coefficient of variation of average specific growth rate was 0.6% (<7%). Hence, fulfilling the all the validity criteria of the test. HPLC method was used for method validation and active ingredient analysis along with stability of the test item in the test medium. Test item was found to be stable in the test medium. The active ingredient content results were considered acceptable (80-120%) as during main study 0 hr and 72 hr avg. recovery for 0.8, 3.2, 12.8 mg/L conc were 94.34%, 94.44%, 95.84% & 94.11%, 94.59%, 96.11%, respectively, were found in acceptable range. Continuous light having and average light intensity of 6766-6794 Lux, pH of 7.6-8.1, temperature 21.7-23.9 °C along with a shaking speed of 110 RPM were provided and maintained for the test system throughout the test. 72h EC50 (growth rate and yield) values with 95% confidence limits were calculated by probit analysis. NOEC and LOEC of growth rate and yield were calculated by one way ANOVA (Kruskal-Wallis-Comparison Z-Value Test) using NCSS Software 2019, version 19.0.3. The cells were counted using Haemocytometer under illumination of the microscope at 24, 48, and 72 h after inoculation. 72-h EC50 of test item to alga on growth rate and yield are 6.19, 2.73 mg/L, respectively. 72-h LOEC of test item to alga on growth rate and yield is 3.2 mg/L. 72-h NOEC of test item to alga on growth rate and yield is 1.6 mg/L. Thus based on the outcomes test chemical was classified into aquatic chronic category 2 as CLP classification criteria.
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.