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EC number: 200-198-0 | CAS number: 54-21-7
- 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:
- weight of evidence
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- Experimental test result using OECD guideline.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- GLP compliance:
- no
- Analytical monitoring:
- no
- Details on sampling:
- Storage Conditions
Store in cool place. Keep container tightly closed in a dry and well-ventilated place. Substance is Hygroscopic. - Vehicle:
- yes
- Details on test solutions:
- The test test chemical was prepared by adding 60 mg of test substance in 300 ml of BBM to get the final concentration of 200 mg/L. The remaining test solutions were prepared by dilution from the above stock solution. To have a better growth and visibility of cells, the initial cell density of the culture was kept 1 X 10E4 cells/ml. Care was taken to have a homogeneous solution for the experiment.
- Test organisms (species):
- Chlorella vulgaris
- Details on test organisms:
- The fresh water green alga Chlorella vulgaris, was used as the test organism. Sterile, unicellular, liquid cultures of algae.
The culture was examined under the microscope to confirm that it was unicellular, healthy and not contaminated.
The medium to be used for the growth of algae was Bold’s Basal Medium (BBM). It is a medium composed of macronutrients, micronutrients, alkaline EDTA solution and Iron solution. Stock solution of each of these was prepared separately and then a complete medium was prepared and sterilized - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 24 °C ±2°C.
- pH:
- 6.7 to 7.4
- Nominal and measured concentrations:
- 12.5 mg/l, 25 mg/l, 50 mg/l, 100 mg/l and 200 mg/l
- Details on test conditions:
- Light Quality White Fluoroscent Light
Light Intensity 1500Lux
Photoperiod 16 Hour Light Period :6 Hour Dark Period
RPM Speed 120 Revolutions per minute
Water Deionized Waer
Test vessel size 100ml
Test solution volume 60ml
Dilution water Bold’s Basal Medium
Test concentration Six test concentration were:
Replicates per concentration
Three replicates for Control
Two replicates for each test concentration - Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 75.25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: calculated from equation through probit analysis
- Details on results:
- The microscopic observations were also noted in each of the experimental flasks. All the cells appeared healthy, round and green throughout the test duration in the control and in the experimental flask also no significant changes were observed.
- Validity criteria fulfilled:
- yes
- Conclusions:
- After 72 hours of exposure to test substance to various nominal test concentration, EC50 calculated from probit analysis was observed to be 75.25 mg/L.
- Executive summary:
This study was designed to assess the effect of the test substance on the growth of green alga Chlorella vulgaris. The study was conducted in accordance with “OECD guideline for testing of chemicals No. 201 – Alga growth inhibition test”.
The effect of test substance was studied on the growth of fresh water green alga Chlorella vulgaris.The study was conducted following OECD guideline 201- Alga growth inhibition test. The test concentration chosen for the study were 12.5 mg/l, 25 mg/l, 50 mg/l, 100 mg/l and 200 mg/l were prepared using stock solution of the test substance using de-ionized water. The green alga was exposed to the test concentration for a period of 72 hours to observe average specific growth rate and % growth inhibition under the effect of test substance. EC50 calculated from probit analysis was observed to be 75.25 mg/L. As the test chemical is readily biodegradable, it cannot be classfied as per CLP classification category.
Reference
Table 1: Showing the average cell count using Haemocytometer of the experimental flasks at an equal interval of 24hrs, 48hrs and 72hrs
Experimental Flasks and test concentration |
24 Hours |
48 Hours |
72 Hours |
Control |
|||
Replicate 1 |
39 x 104 |
41.5 x 104 |
47 x 104 |
Replicate 2 |
28 x 104 |
46.5 x 104 |
34 x 104 |
Replicate 3 |
34 x 104 |
42.5 x 104 |
44 x 104 |
CAS No. 54-21-7 |
|||
12.5 mg/l |
|||
Replicate 1 |
27 x 104 |
17 x 104 |
19.5 x 104 |
Replicate 2 |
27.5 x 104 |
20.5 x 104 |
12 x 104 |
25 mg/l |
|||
Replicate 1 |
10.5 x 104 |
16 x 104 |
14.5 x 104 |
Replicate 2 |
12.5 x 104 |
18.5 x 104 |
15.5 x 104 |
50 mg/l |
|||
Replicate 1 |
28.5 x 104 |
11.5 x 104 |
5.5 x 104 |
Replicate 2 |
22 x 104 |
12.5 x 104 |
10 x 104 |
100 mg/l |
|||
Replicate 1 |
22.5 x 104 |
3.5 x 104 |
6 x 104 |
Replicate 2 |
35 x 104 |
6 x 104 |
3.5 x 104 |
200 mg/l |
|||
Replicate 1 |
20 x 104 |
22 x 104 |
2.5 x 104 |
Replicate 2 |
24.5 x 104 |
22 x 104 |
7 x 104 |
Table 2 : Showing the values of average specific growth rate and percentage inhibition after an interval of 72 hours
|
CONTROL |
12.5 mg/l |
25 mg/l |
50 mg/l |
100 mg/l |
200 mg/l |
||||||
Average Specific Growth rate (µ ) |
R1 |
1.283 |
R1 |
0.990 |
R1 |
0.891 |
R1 |
0.568 |
R1 |
0.597 |
R1 |
0.305 |
R2 |
1.175 |
R2 |
0.828 |
R2 |
0.913 |
R2 |
0.767 |
R2 |
0.417 |
R2 |
0.648 |
|
R3 |
1.261 |
|
||||||||||
Mean of Avg. Specific growth rate |
1.240 |
0.909 |
0.902 |
0.667 |
0.507 |
0.477 |
||||||
Percentage Inhibition (%I) |
_ |
26.69 |
27.26 |
46.21 |
59.11 |
61.53 |
Table 3 : Depicting pH values at test initiation (0 Hours) and test termination ( 72 Hours)
Experimental Flasks and test concentration |
0 Hours |
72 Hours |
CONTROL |
||
Replicate 1 |
7.3 |
7.4 |
Replicate 2 |
7.2 |
7.3 |
Replicate 3 |
7.4 |
7.5 |
CAS No. 54-21-7 |
||
12.5 mg/l |
||
Replicate 1 |
7.3 |
7.2 |
Replicate 2 |
7.0 |
7.2 |
25 mg/l |
||
Replicate 1 |
7.3 |
7.4 |
Replicate 2 |
7.4 |
7.3 |
50 mg/l |
||
Replicate 1 |
7.2 |
7.2 |
Replicate 2 |
7.1 |
7.1 |
100 mg/l |
||
Replicate 1 |
7.0 |
7.1 |
Replicate 2 |
7.1 |
7.2 |
200 mg/l |
||
Replicate 1 |
7.2 |
7.1 |
Replicate 2 |
7.1 |
7.1 |
Description of key information
This study was designed to assess the effect of the test substance on the growth of green algaChlorella vulgaris. The study was conducted in accordance with “OECD guideline for testing of chemicals No. 201 – Alga growth inhibition test”.
The effect of test substance was studied on the growth of fresh water green alga Chlorella vulgaris. The study was conducted following OECD guideline 201- Alga growth inhibition test. The test concentration chosen for the study were 12.5 mg/l, 25 mg/l, 50 mg/l, 100 mg/l and 200 mg/l were prepared using stock solution of the test substance using de-ionized water. The green alga was exposed to the test concentration for a period of 72 hours to observe average specific growth rate and % growth inhibition under the effect of test substance. EC50 calculated from probit analysis was observed to be 75.25 mg/L. As the test chemical is readily biodegradable, it cannot be classfied as per CLP classification category.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 75.25 mg/L
Additional information
Various experimental of test chemical and its read across chemicals have been reviewed to determine the toxicity of target to aquatic algae and their results are summarized below.
The first Experimental study performed for the target chemical and it was designed to assess the effect of the test substance on the growth of green algaChlorella vulgaris. The study was conducted in accordance with “OECD guideline for testing of chemicals No. 201 – Alga growth inhibition test”.
The effect of test substance was studied on the growth of fresh water green algaChlorella vulgaris.The study was conducted following OECD guideline 201- Alga growth inhibition test. The test concentration chosen for the study were 12.5 mg/l, 25 mg/l, 50 mg/l, 100 mg/l and 200 mg/l were prepared using stock solution of the test substance using de-ionized water. The green alga was exposed to the test concentration for a period of 72 hours to observe average specific growth rate and % growth inhibition under the effect of test substance. EC50 calculated from probit analysis was observed to be 75.25 mg/L. As the test chemical is readily biodegradable, it cannot be classfied as per CLP classification category.
Next experimental study was reviewed from handbook in this the green algae were exposed to the test concentration for a period of 14 days to observe average specific growth rate. On the basis of growth rate EC50 value was determined to be 60 mg/L for 3 hrs and > 10 mg/L for 14 days.
Last experimental study was also reviewed from handbook and this study was designed to assess the effect of the test substance on the growth of green algae Haematococcus pluvialis. The green algae were exposed to the test concentration for a period of 4 hr to observe average specific growth rate. On the basis of growth rate EC10 value was determined to be165 mg/L .
By considering results of all the studies mentioned above it is concluded that EC50 value of test chemical is in range from 60 mg/L to 165 mg/L. On the basis of this range value and ready biodegradability test chemical is considered to be non toxic and cannot be classified as per CLP regulation.
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