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EC number: 700-342-7 | CAS number: 1163775-81-2
- 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:
- 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- GLP compliance:
- yes
- Specific details on test material used for the study:
- N/A
- Analytical monitoring:
- yes
- Details on sampling:
- N/A
- Vehicle:
- no
- Details on test solutions:
- N/A
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Green algae
- Strain: Pseudokichneriella subcapitata (ID: PS-IHB-140104)
- Source (laboratory, culture collection): institute of hydrobiology, Chinese Academy of Sciences
- Method of cultivation: The algae were inoculated in 250 mL glass flasks with a concentration of 10^4 cells/mL, incubated during 3 days and then inoculated to another flask. At the beginning of the test, the algae were in the exponential growth phase when inoculated into the test solutions.
ACCLIMATION
- Acclimation period: The algae were inoculated in 250 mL glass flasks with a concentration of 10^4 cells/mL, incubated during 3 days and then inoculated to another flask. At the beginning of the test, the algae were in the exponential growth phase when inoculated into the test solutions. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Post exposure observation period:
- none
- Hardness:
- no details mentioned
- Test temperature:
- 23.2 - 23.6 °C
- pH:
- 8.02 - 9.33
- Dissolved oxygen:
- not mentioned
- Salinity:
- N/A
- Conductivity:
- N/A
- Nominal and measured concentrations:
- Nominal: 100 mg/L
measured concentration below the limit of detection (LOD = 0.214 mg/L) - Details on test conditions:
- lnoculation and incubation
An inoculum culture in the test medium was pre-cultured for 3 days before start of the test under the test conditions. At the begining of the test, the alga was in the exponential growth phase when inoculated to the test solutions and the density of the alga was 9.103 x 10^5/mL. For the treatment group, 3.30 mL of the alga culture were inoculated into 300mL of test solution and the initial cell density of the test solution was about 10^4 /mL (for the control cultures, 6.59 mL of the alga culture were inoculated into 600mL of alga medium). 100mL of test solution was added into each of 250 mL glass conical flasks.
Conditions of incubation
Each flask was then capped with Parafilm and put in a culturing chamber by shaking at a speed of 130rpm.
Temperature: 23.2°C-23.6°C.
Illumination: the surface where the cultures are incubated received continuous, uniform fluorescent illumination at equivalent range of 5614-5842 lux for cool white light. Any differences from the selected light intensity over the test area did not exceed the range of ±15%.
Observation and measurements
The algal biomass in each vessel was determined by a cell counter at the beginning and the end of the test. The light density was determined at 0, 24, 48 and 72h during the test period. At the beginning of the test, pH values for the control and each test concentration were measured using the remaining test solutions. At the end of the test, one vessel was randomly taken from each treatment group and the control group for pH measurement and microscopic observation of the algae. The concentrations of the test substance were determined at 0 and 72h of the test. 10 mL of test solution was taken from one test vessel of each concentration. Before sampling, separation of algae from the test medium was made by syringe filters.
- Test vessel: sterile-aerated Erlenmeyes flasks
- Initial cells density: 10000 cells/mL
- Control end cells density: 1162833 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per vehicle control (replicates): not applicable
GROWTH MEDIUM
- Standard medium used: yes
Analytical grade salts were dissolved in deionised water to obtain separate alga medium stock solutions. The stock solutions were filtrated with 0.22 µm filter membrane and kept at 2-8 °C. The alga medium was prepared by diluting the stock solutions in deionised water shortly before the test began.
TEST MEDIUM / WATER PARAMETERS
no details mentioned
OTHER TEST CONDITIONS
Illumination: the surface where the cultures are incubated received continuous, uniform fluorescent illumination at equivalent range of 5614-5842 lux for cool white light. Any differences from the selected light intensity over the test area did not exceed the range of ±15%.
At the beginning of the test, pH values for the control and each test concentration were measured using the remaining test solutions. At the end of the test, one vessel was randomly taken from each treatment group and the control group for pH measurement and microscopic observation of the algae.
- Sterile test conditions: yes
- Adjustment of pH: not adjusted
- Light intensity and quality: approx. 5614-5842 lux, white
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Cell numbers for exposure times of 0, 24, 48, 72h
- Chlorophyll measurement: no
- Other: none
- Range finding study: The test substance is insoluble. A nominal concentration of 100mg/L was prepared and stirred (via magnetic stirrer) for 72h at 500rpm in the dark, and then filtered with 0.45µm nitrocellulose membrane to prepare the saturated solution under test conditions. One nominal concentration of the saturated solution was used in the range-finding test. Three replicates were included for each treatment as well as six for the control with alga medium. The test duration was 72h.
In the range-finding test, there was no statistically significant difference in alga growth between the treatment group and the control one (P=0.8199 for average specific growth rate and P=0.7855 for yield, 19.2). Therefore, a limit test would be performed. - Reference substance (positive control):
- no
- Key result
- 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:
- other: not toxic in the range of water solubility
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): no observations made
- 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
- Effect concentrations exceeding solubility of substance in test medium: no - Results with reference substance (positive control):
- no reference substance tested
- Reported statistics and error estimates:
- no statistical evaluation performed
- Validity criteria fulfilled:
- yes
- Remarks:
- mean biomass control cultures increased 157 fold, mean coefficient of variation section-by-section specific growth rates control cultures 12.5%, coefficient of variation of average specific growth rates test period in replicate control cultures 1.1 %
- Conclusions:
- Not toxic to algae under test conditions in the range of water solubility.
- Executive summary:
The growth inhibition effect of 1,2,4 -Benzenetricarboxylic acid, mixed dodecyl and octyl triesters to Pseudokirchneriella subcapitata was determined in a 72h test according to OECD 201.
A nominal concentration of 100 mg/L of the test substance was prepared and stirred for 72 h at 500 rpm in the dark followed by filtration using a 0.45 µm nitrocellulose membrane to make a saturated solution of test system (referred to as "saturated "solution" in this report, since the measured concentration was below LOD, LOD = 0.214 mg/L). Based on the results of the range-finding test, one treatment group of saturated solution and one control group of alga medium were included in the limit test. Six replicates for each group were run. The duration was 72h.
The mean biomasss of the control cultures was increased by 157 folds, which is higher than the validity criterion of at least 16 within the 72h test period., corresponding to a specific growth rate of 0.92 day-1 . The mean coefficient of variation for section-by-section specific growth rates in the control cultures was 12.5 %, which was below 35 %. The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures was 1.1%, which was below 7 %. Hence, the test was cosidered to be valid. During the test, the measured concentrations of the tst substance analyzed by gas chromatography were below the limit of detection (LOD, LOD=0.214 mg/L).
Under the present test conditions, no inhibition effects were observed on Pseudokirchneriella subcapitata exposed to the test substance. Therefore, based on average specific growth rate, the 72h NOEC was not less than the measure concentration of the saturated solution, the LOEC were also higher than the measured concentration of the saturated solution. The concentration was below LOD, LOD=0.214 mg/L.
Not toxic to algae under test conditions in the range of water solubility.
Reference
Table 1: Cell density (cell /ml) of Pseudokirchneriella subcapitata exposed to the test substance for 72h in the limit test:
Group | 0h | 24h | 48h | 72h | |
Blank control | 1 | 10000 | 60300 | 379500 | 1435000 |
2 | 10000 | 58470 | 366800 | 1623000 | |
3 | 10000 | 62720 | 370300 | 1554000 | |
4 | 10000 | 57910 | 391800 | 1686000 | |
5 | 10000 | 62430 | 357600 | 1538000 | |
6 | 10000 | 62550 | 346600 | 1609000 | |
Mean | 10000 | 60730 | 368767 | 1574167 | |
CV (%) | 0 | 3.56 | 4.3 | 5.48 | |
Treatment group /saturated solution) | 1 | 10000 | 63180 | 372300 | 1551000 |
2 | 10000 | 60370 | 369100 | 1546000 | |
3 | 10000 | 59970 | 351500 | 1577000 | |
4 | 10000 | 62640 | 364400 | 1589000 | |
5 | 10000 | 58300 | 359500 | 1518000 | |
6 | 10000 | 59130 | 353100 | 1515000 | |
Mean | 10000 | 60598 | 361650 | 1549333 | |
CV (%) | 0 | 3.19 | 2.34 | 1.94 |
Table 2: Growth of Pseudokirchneriella subcaptitata for the blank control cultures in the limit test
Blank Control | Average specific growth rate | Yield | |||||
0 - 24h | 24 - 48h | 48 - 72h | CV (%) for Section-by-section | 0 - 72 h | |||
1 | 1.80 | 1.84 | 1.33 | 17.1 | 1.66 | 1425000 | |
2 | 1.77 | 1.84 | 1.49 | 10.9 | 1.70 | 1613000 | |
3 | 1.84 | 1.84 | 1.43 | 12.9 | 1.68 | 1544000 | |
4 | 1.76 | 1.91 | 1.46 | 13.5 | 1.71 | 1676000 | |
5 | 1.83 | 1.75 | 1.46 | 11.6 | 1.68 | 1528000 | |
6 | 1.83 | 1.71 | 1.54 | 8.9 | 1.69 | 1599000 | |
Mean | 1.80 | 1.80 | 1.54 | 12.5 | 1.69 | 1564167 | |
CV (%) for replicates | 1.99 | 4.05 | 4.72 | - | 1.10 | 5.51 |
Table 3: Growth of Pseudokirchneriella subcapitata exposed to the test substance in the limit test
Treatment group | Avergae specific growth rate | Yield | ||||||
0 -24 h | 24 -48h | 48 -72h | 0 -72h | 72 h Inhibition |
0 -72h |
72 h Inhibition |
||
saturated solution
|
1 |
1.84 |
1.77 |
1.43 |
1.68 |
0.27 |
1541000 |
1.48 |
2 |
1.80 |
1.81 |
1.43 |
1.68 |
0.33 |
1536000 |
1.80 |
|
3 |
1.79 |
1.77 |
1.50 |
1.69 |
-0.06 |
1567000 |
-0.18 |
|
4 |
1.83 |
1.76 |
1.47 |
1.69 |
-0.21 |
1579000 |
-0.95 |
|
5 |
1.76 |
1.82 |
1.44 |
1.67 |
0.69 |
1508000 |
3.59 |
|
6 |
1.78 |
1.79 |
1.46 |
1.67 |
0.74 |
1505000 |
3.78 |
|
Mean |
1.80 |
1.79 |
1.46 |
1.68 |
0.29 |
1539333 |
1.59 |
|
CV (%) |
1.76 |
1.32 |
1.93 |
0.38 |
- |
1.95 |
- |
Description of key information
1,2,4 -Benzenetricarboxylic acid, mixed dodecyl and octyl triesters under test conditions has shown no toxic effects to Pseudokirchneriella subcapitata in the range of water solubility.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 100 mg/L
Additional information
The growth inhibition effect of 1,2,4 -Benzenetricarboxylic acid, mixed dodecyl and octyl triesters to Pseudokirchneriella subcapitata was determined in a 72h test according to OECD 201.
A nominal concentration of 100 mg/L of the test substance was prepared and stirred for 72 h at 500 rpm in the dark followed by filtration using a 0.45 µm nitrocellulose membrane to make a saturated solution of test system (referred to as "saturated "solution" in this report, since the measured concentration was below LOD, LOD = 0.214 mg/L). Based on the results of the range-finding test, one treatment group of saturated solution and one control group of alga medium were included in the limit test. Six replicates for each group were run. The duration was 72h.
The mean biomasss of the control cultures was increased by 157 folds, which is higher than the validity criterion of at least 16 within the 72h test period., corresponding to a specific growth rate of 0.92 day-1 . The mean coefficient of variation for section-by-section specific growth rates in the control cultures was 12.5 %, which was below 35 %. The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures was 1.1%, which was below 7 %. Hence, the test was cosidered to be valid. During the test, the measured concentrations of the tst substance analyzed by gas chromatography were below the limit of detection (LOD, LOD=0.214 mg/L).
Under the present test conditions, no inhibition effects were observed on Pseudokirchneriella subcapitata exposed to the test substance. Therefore, based on average specific growth rate, the 72h NOEC was not less than the measure concentration of the saturated solution, the LOEC were also higher than the measured concentration of the saturated solution. The concentration was below LOD, LOD=0.214 mg/L.
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