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EC number: - | 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Version / remarks:
- 28 July 2011
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Reaction products of (Z)-octadec-9-enol and lactic acid
- IUPAC Name:
- Reaction products of (Z)-octadec-9-enol and lactic acid
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- Test Substance
Test Substance Name: Dermol OL
CAS Number: 42175-36-0
Batch Number: P7610
Purity: 100 %
Receipt Date: 01 February 2018
Retest Date: January 2020
Storage on Receipt: Room temperature (15 – 30°C)
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- At approximately 24-hour intervals after the start of the incubation period,
pre-determined volumes of test media (1.0 mL at 24 hours and 0.5 mL at 48 and
72 hours) were removed from each incubated test vessel, and transferred to
individually identified cell counting vials. The contents of each vial were diluted to a
10 mL final volume with an electrolyte solution. The cell density of the vial contents
was then determined using a particle counter (Z2 Coulter Counter®).
Test solutions
- Vehicle:
- no
- Details on test solutions:
- Based on the results of the range-finding test the definitive test was conducted with a
control and nominal test concentrations of 1.0, 3.2, 10, 32 and 100 mg/L LR WAF.
The results from the initial definitive test have not been reported.
Six test vessels were prepared for the control (EC medium only) and three replicate
test vessels were prepared for each test concentration, each with an initial cell
concentration of 1 × 104 cells/mL. A blank vessel (not inoculated with algae) was
prepared during the definitive test at control only to establish back ground counts on
the coulter, these counts were later subtracted from the cell counts.
At the start of the test, amounts of test substance (1.03, 3.19, 10.06, 32.21 and
100.80 mg) were separately added to 1000 mL of EC medium, the test substance was
weighed onto a glass slide which was then suspended at the top of the beaker. The
preparations were then stirred for ca 24 hours (with a vortex no deeper than 1 cm),
media were then allowed to settle for ca 1 hour. The final media were then syphoned
from the mid-section (aqueous phase) of the vessels. A control treatment was
prepared in the same manner with EC medium only.
Algae cell counts were performed at 24, 48 and 72 hours during the test.
Test organisms
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- The test organism, Pseudokirchneriella subcapitata (Strain 278/4), was originally
obtained from the Culture Collection of Algae and Protozoa (CCAP) and is a
representative species of the freshwater aquatic phytoplankton. This species is
recommended for testing in accordance with the OECD regulatory guidelines.
Prior to testing, duplicate starter cultures were prepared and incubated under test
conditions to obtain sufficient algal cells in exponential
growth and to achieve a starting algae cell density of 1 × 104 cells/mL.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
Test conditions
- Test temperature:
- 22.3-23.1°C
- Nominal and measured concentrations:
- nominal test concentrations of 1.0, 3.2, 10, 32 and 100 mg/L LR WAF (loading rate water
accommodated fraction). - Details on test conditions:
- [
- Reference substance (positive control):
- yes
- Remarks:
- [State positive control substance]
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 0.599 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 0.604 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: area under the growth curve
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 0.875 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- ca. 0.32 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- ca. 0.1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: area under the growth curve
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- ca. 0.32 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The effects of Dermol OL on the growth of the unicellular green alga,
Pseudokirchneriella subcapitata, were determined during a 72-hour growth inhibition
toxicity test conducted in accordance with OECD Chemicals Testing Guideline
No. 201 Alga, Growth Inhibition Test (adopted 23 March 2006) (Annex 5 corrected
28 July 2011)
Given that the test substance is a multi-constituent substance, the results are based on
nominal loading rates.
Based on nominal loading rate concentrations, the 72-hour EyL50 and ErL50 values
were calculated to be 27.9 mg/L and 50.1 mg/L, respectively.
The corresponding NOEL values for yield and specific growth rate after 72 hours
were 10 and 32 mg/L, respectively.
All validity criteria were met therefore the test was considered valid.
- Executive summary:
The objective of the study was to determine the effects of the test substance against
algal growth by exposing the green alga, Pseudokirchneriella subcapitata, at the
exponential growth phase to the test substance during a 72-hour test period.
The test was conducted in accordance with OECD Chemicals Testing Guideline No.
201. Alga, Growth Inhibition Test (adopted 23 March 2006, Annex 5 corrected 28
July 2011).
The test substance Dermol OL is a multi-constituent substance with low water
solubility and as such falls into the category of a “difficult substance” as defined by
the OECD Guidance Document (OECD Series on Testing and Assessment, No. 23
(2000); Guidance Document on Aquatic Toxicity Testing of Difficult Substances and
Mixtures). Based on the recommendations of this guideline, the test substance was
prepared as Water Accommodated Fractions (WAFs).
Based on the results of a range-finding test and two initial definitive test, for which
the key results only have been reported, the definitive test was conducted at nominal
test concentrations of 1.0, 3.2, 10, 32 and 100 mg/L LR WAF (loading rate water
accommodated fraction). Six replicate vessels were prepared for the control and three
replicate vessels were prepared for the test concentrations.
Test vessels (250 mL conical flasks) were prepared containing 100 mL of the
appropriate test or control medium. Each test vessel was inoculated with
1 × 104 algae cells/mL and incubated at 21 – 24°C (under 4440 – 8880 Lux light
intensity) for 72 hours with cell counts at 24-hour intervals.
Chemical analysis was conducted on fresh media at 0 hours and the corresponding old
media at 72 hours. Analysis of the test samples at 0 and 72 hours are summarised in
the table below.
Given that the test substance is a multi-constituent substance, the results are based on
nominal loading rates.
Nominal Concentration(mg/L) Measured Concentration (mg/L)
0 hours (new) 72 hours (old)
Control - -
1.0 0.0150 <LOQ
3.2 0.0710 <LOQ 10 0.0302 <LOQ
32 0.104 <LOQ
100 0.366 0.348
LOQ = 0.005 mg/L (LOQ = limit of quantification)
- None detected
The 72-hour yield (EyLx), area under the growth curve (EbLx) and growth rate (ErLx)
toxicity values, with corresponding no observed effect loading rates (NOEL) are
presented in the table below.
Parameter 72 hours
Confidence limits (LUL-UCL) Statistical test Growth rate ErL10
ErL20
ErL50
NOEL
18.7
33.0
50.1
32
9.4 -33.8
18.9 -38.7
45.0 -55.4
NC
Liner Interpolatin
(ICPIN)
Derived empirically
Yield EyL10
EyL20
EyL50
NOEL
11.3
14.2
27.9
10
Na-14.4
0.86 -18.6
15.7 -42.8
NC
Liner Interpolation
(ICPIN)
Derived empirically
NC Not calculated
NA Not applicable
LCL Lower confidence limits
UCL Upper confidence limits
Based on nominal
loading rates, the 72-hour EyL50 and ErL50 values were calculated to
be 27.9 mg/L and 50.1 mg/L, respectively.
The corresponding NOEL values for yield and specific growth rate after 72 hours
were 10 and 32 mg/L, respectively.
All validity criteria were met therefore the test was considered valid.
]
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