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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 701-177-3 | 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:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 20 °C
- Nominal and measured concentrations:
- Nominal: Control, 0.16, 0.31, 0.63, 1.25, 2.50, 5.0, 10.0, 20.0 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer flasks
- Size, fill volume: 250 mL, 100 mL
- Initial cells density: 10,000 cells/mL
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): no data
GROWTH MEDIUM
- Standard medium used: yes, OECD medium
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: fluorimeter measurements
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2 - Reference substance (positive control):
- no
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 5.1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC20
- Effect conc.:
- 1.57 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 21 Jul - 24 Jul 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- adopted in 2006
- Deviations:
- yes
- Remarks:
- Higher test temperature (guideline: max. 24 °C; test: max. 29 °C)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- adopted in 2008
- Deviations:
- yes
- Remarks:
- Use of 64 mg FeCL3*6H2O/L instead of 80 mg/L.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Landesamt für Umwelt, Wasserwirtschaft und Gewerbeaufsicht, Mainz, Germany
- Analytical monitoring:
- yes
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution containing 10 g/L was prepared using the following procedure: 10 g test item was mixed with 1.1 g NaOH (45%). 40 mL deionised water (80 – 100 °C) was added. After homogenisation with a glass stirrer, 85 mL deionised water (room temperature) was added. Then, the vessel was stirred on a magnetic stirrer. 0.5 M NaOH was added until the resulting solution was clear. The pH of the solution was adjusted to 7.8 ± 0.2 with 1 M HCl. the solution was transferred into a volumetric flask and filled up to 1000 mL with deionised water. From this stock solution, the concentrations to be tested were prepared by diluting with deionised water. - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Strain: Chodat
- Source (laboratory, culture collection): The culture of Desmodesmus subspicatus was obtained in June 2010 by MBM Science Bridge GmbH (Institut für Pflanzenphysiologie, Universität Göttingen).
- Age of inoculum (at test initiation): 5 days
- Method of cultivation: The algae are kept as stock culture on solid agar at 8 °C. From an aliquot of this stock culture, the pre-culture was prepared. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 26 - 29 °C
- pH:
- 7.6 - 8.8
- Nominal and measured concentrations:
- Nominal: 0, 0.22, 0.46, 1.0, 2.2, 4.6, 10, 22, 46 mg/L
Measured (initial): < LOD, 0.37, 0.42, 0.53, 0.91, 2.01, 4.35, 11.32, 24.55 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: Round cuvettes of 10 mm diameter
- Aeration: None, magnetic stirring
- Initial cells density: 2.2E04 cells/mL
- Control end cells density: 180E04 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Deionised water
- Intervals of water quality measurement: Temperature was measured every 24 h, pH was measured at test start and test end.
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Light intensity and quality: 5900 - 6100 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Cell numbers were determined by photometric measurement
TEST CONCENTRATIONS
- Spacing factor for test concentrations: approx. 2.1
- Range finding study
- Test concentrations: 0.08, 0.125, 0.2, 0.32, 0.5, 0.8, 1.25, 2.0, 3.2 mg/L - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 6.3 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% CL = 5.1 - 8.7 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.91 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.3 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 95% CL = 2.0 - 2.6 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.53 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.7 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Remarks on result:
- other: 95% Cl = 2.3 - 3.2 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.91 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Details on results:
- - Exponential growth in the control (for algal test): yes, increase factor of 82
- All validity criteria of the guideline are fulfilled.
- Microscopical observations: Normal growth up to 10 mg/L, no cells in the 22 and 46 mg/L treatments
- Observation of abnormalities (for algal test): Treatments 22 and 46 mg/L showed clouded test solution
- Analytical measurements: The recovery rates at test start ranged between 44 and 170%. After 72 h, only in the two highest treatments 2 - 20% of nominal values could be detected. Therefore the measured start concentration was used for the determination of the results.
Referenceopen allclose all
Table 1: Fluorimeter measurements at test start and after 72 h of exposure
Concentration (mg/L) |
Fluorimeter measurement (% of control) |
|
0 h |
72 h |
|
Control |
- |
- |
0.16 |
94.74 |
109.02 |
0.31 |
101.75 |
94.00 |
0.63 |
91.23 |
87.95 |
1.25 |
105.26 |
82.16 |
2.5 |
101.75 |
73.77 |
5.0 |
94.74 |
50.36 |
10.0 |
101.75 |
32.48 |
20.0 |
105.26 |
29.37 |
Inhibition
Nom. Conc. in mg/L |
Measured Conc. in mg/L |
% Inhibition |
||
Growth Rate µ |
Area under the Curve AUC |
Yield |
||
0 |
0 |
0 |
0 |
0 |
0.22 |
0.37 |
-0.14 |
-0.72 |
-0.62 |
0.46 |
0.42 |
-0.63 |
-0.72 |
-2.83 |
1.0 |
0.53 |
0.20 |
2.98 |
0.90 |
2.2 |
0.91 |
0.74 |
10.61 |
3.24 |
4.6 |
2.0 |
10.93 |
45.19 |
38.25 |
10 |
4.4 |
32.35 |
79.09 |
76.71 |
22* |
11.3 |
39.51 |
62.70 |
83.46 |
46* |
24.6 |
25.04 |
-10.00 |
67.61 |
*Treatments 22 and 46 mg/L showed clouded test solution, photometric measurement not evaluable.
Measured Concentrations in mg/L and corresponding Recovery Rates in %
Nom. Conc. in mg/L |
Measured Conc. 0h in mg/L |
% Nom. Conc. |
Measured Conc. 72 h in mg/L |
& Nom. Conc. |
% Recovery |
0 |
-- |
-- |
-- |
-- |
-- |
0.22 |
0.37 |
170 |
-- |
-- |
-- |
0.46 |
0.42 |
91 |
-- |
-- |
-- |
1 |
0.53 |
53 |
-- |
-- |
-- |
2.2 |
0.91 |
42 |
-- |
-- |
-- |
4.6 |
2.01 |
44 |
-- |
-- |
-- |
10 |
4.35 |
44 |
-- |
-- |
-- |
22 |
11.32 |
51 |
0.35 |
2 |
3 |
46 |
24.55 |
53 |
9 |
20 |
37 |
Description of key information
ErC50 (72h) > 4.4 mg/L; NOErC = 0.91 mg/L for Desmodesmus subspicatus (OECD 201)
Key value for chemical safety assessment
Additional information
Two studies investigating the toxicity to aquatic algae of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine (EC 701-177-3) are available.
The key study was carried out according to OECD guideline 201 under GLP conditions including analytical measurement. In this static test, Desmodesmus subspicatus was exposed to eight test concentrations (0.22, 0.46, 1.0, 2.2, 4.6, 10, 22 and 46 mg/L). Analytical measurements verified the test item concentration to be 44 – 170% of the nominal test concentration at test start for all eight concentrations. The effect concentrations were based on the initial test concentrations. Only for the two highest test concentrations analytical measurements were done after 72h. In these two highest test concentrations (nominal: 22 and 46 mg/L) a recovery of 3 and 37% respectively was determined. But as turbidity was observed for these both highest test concentrations, they were not evaluated as reliable as photometric measurement was not evaluable. In addition, it could not be excluded that these are physical effects due to the undissolved test material. In the study report an EC 50 of 6.3 mg/L for growth rate was reported although the inhibition is below 50% for the highest reliable test concentration (32.35% for 10 mg/L nominal = 4.4 mg/L measured). Thus, an EC50 > 4.4 mg/L for growth rate is stated. The NOEC is reported as 0.91 mg/L (measured).
The supporting study was carried out under non-GLP conditions similar to OECD guideline 201 and without analytical measurement. Desmodesmus subspicatus was exposed to eight test concentrations (0.16, 0.31, 0.63, 1.25, 2.50, 5.0, 10.0, 20.0 mg/L) under static conditions. An EbC20 (72h) of 1.57 mg/L and an EbC50 (72h) of 5.1 mg/L was determined based on biomass.
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.